-------
3.3.2 Motor Vehicle Emissions Sources
Like industrial emissions sources, motor vehicles contribute significantly to air pollution
in urban environments, so thorough analyses of urban air monitoring data must consider
contributions from motor vehicle sources. Pollutants found in motor vehicle exhaust generally
are combustion products or result from incomplete combustion of vehicle fuels. Although
modern vehicles and, more recently, vehicle fuels have been engineered to minimize air
emissions, all motor vehicles with internal combustion engines emit a wide range of chemical
pollutants. The magnitude of these emissions in urban areas primarily depends on the volume of
traffic, while the chemical profile of these emissions depends more on vehicle design and fuel
content. Several studies have generated chemical profiles of motor vehicle exhaust (Conner
et al., 1995), and such profiles provide additional context for analyzing spatial variations in
ambient air monitoring data.
3.3.3 Natural Emissions Sources
Many natural processes release volatile compounds to the air. These processes include,
but are not limited to, natural decay and biosynthesis in oceans and forests, fires in forests and
grasslands, and volcanic eruptions. Some studies have reported that natural emissions may
exceed both industrial and motor vehicle emissions on a global scale. In urban areas, however,
the contributions of industrial and motor vehicle sources to air pollution probably outweigh the
contribution of natural emissions. Accordingly, the data interpretations throughout this report
focus on how emissions from motor vehicles and industry affect air quality, with a much lighter
emphasis on the effect of emissions from natural sources.
3.3.4 Atmospheric Fate and Transport
Atmospheric fate and transport processes provide the link between emissions and ambient
air quality. More specifically, atmospheric dispersion and photochemical reactions primarily
determine the fate of chemicals emitted into the air. Atmospheric dispersion refers to the natural
phenomena by which chemical emissions gradually move to regions of lower concentration by
convection and diffusion. The rate at which emissions disperse depends on characteristics of the
3-12
-------
emissions source (such as stack height and exit velocity) and on local meteorological conditions
(such as cloud cover and wind velocity). Photochemical reactions both consume and produce
pollutants in urban environments, and rates for the various reactions vary with temperature, solar
radiation, and chemical composition.
Because atmospheric dispersion and photochemical reactions strongly affect the
composition and magnitude of air pollution, both factors should be considered in a thorough
review of ambient air monitoring data. Although sophisticated fate and transport computer
models allow for a detailed quantitative analysis of these factors (USEPA, 1986), extensive
site-specific modeling analyses are beyond the scope of this report.
3-13
-------
4.0 Summary of 1998 UATMP Data
This section uses four parameters—prevalence, concentration range, central tendency, and
variability—to provide an overview of the ambient air monitoring data collected during the 1998
UATMP. Sections 5 through 8 present more detailed interpretations of the trends and
correlations in the 1998 UATMP data. Refer to the appendices for a complete presentation of the
data:
• Appendix D: Summary Tables for VOC Monitoring
• Appendix E: Summary Tables for Carbonyl Monitoring
• Appendix F: VOC Raw Monitoring Data
• Appendix G: Carbonyl Raw Monitoring Data
4.1 Data Summary Parameters for VOCs
Tables D-l through D-12 in Appendix D use the four data summary parameters defined
above to summarize the VOC monitoring results for the 1998 UATMP. The following paragraphs
review the basic findings indicated by the VOC data summary tables.
4.1.1 Prevalence
While the prevalence of VOCs in ambient air varied significantly from compound to
compound and from monitoring location to monitoring location, the majority of VOCs were
present at a prevalence greater than 75 percent at most of the monitoring locations. To simplify
data presentation and interpretation, for the purposes of this report, program-wide prevalent
compounds were identified within each compound group (hydrocarbons, halogenated
hydrocarbons, polar compounds, and carbonyls). As discussed in Section 3.1.1, the most
4-1
-------
program-wide prevalent compounds are defined as the top compounds measured across the
sampling sites in both number of nondetects and percentage contribution. The analyses and
interpretations throughout this report focus primarily on these most program-wide prevalent
compounds. For the 1998 UATMP, the program-wide prevalent VOCs are:
HYDROCARBONS
Acetylene
Benzene
Ethylbenzene
m-,p-xy\ene
o-xylene
Propylene
Toluene
«ALOGENATO> HYDROCARBONS
Carbon Tetrachloride
Chloromethane
/7-Dichlorobenzene
Dichlorodifluoromethane
Methylene Chloride
Tetrachloroethylene
1,1,1 -Trichloroethane
Trichlorofluoromethane
Trichlorotrifluoroethane
POLARCOMPOUNDS
Acetonitrile
Methyl Ethyl Ketone
Methyl tert-Butyl Ether
Because these compounds were consistently present at detectable levels, the UATMP
monitoring data characterize ambient levels for these compounds much more accurately than they
4-2
-------
characterize ambient levels for the VOCs with lower prevalence. Further, the high prevalence
allows for a meaningful statistical analysis of data correlations and a thorough review of spatial
variations and temporal variations in ambient air quality.
Readers interested in examining data trends for the less program-wide prevalent
compounds more closely should refer to the summary tables in Appendix D and the raw
monitoring data in Appendix F, but also should note the limitations posed by data sets with many
nondetect observations.
4.1.2 Concentration Range
To efficiently summarize the concentration ranges cited in Appendix D, Table 4-1
indicates the number of monitoring stations that detected peak VOC concentrations within certain
ranges. These data show that peak concentrations, like prevalence, varied significantly among
compounds and monitoring stations. During the 1998 UATMP, measured ambient air
concentrations of more than 80 percent of the VOCs identified by the analytical method never
exceeded 1 ppbv. Specifically:
More than 85 percent of the hydrocarbon compounds identified by the analytical method
never exceeded 5 ppbv. Only w-octane never exceeded 1 ppbv.
More than 94 percent of the halogenated hydrocarbon compounds identified by the
analytical method never exceeded 1 ppbv; 99 percent never exceeded 5 ppbv. Only
chloromethane and methylene chloride exceeded Ippbv in greater than 50 percent of the
samples.
More than 70 percent of the polar compounds identified by the analytical method never
exceeded 1 ppbv; more than 90 percent never exceeded 5 ppbv. Only methyl ethyl ketone
exceeded 1 ppbv in 100 percent of the samples at all sampling locations.
4-3
-------
4.1.3 Central Tendency
Figures 4-1 through 4-3 illustrate how central tendency concentrations for the program-
wide prevalent VOCs varied from one monitoring location to the next. Although the spatial
variations differ for each compound, the figure indicates several general data trends:
in
p" ' i ""as.*" v*"'' -«.' . '
re makmg any comparisons.
-^*-^ '*-',^ ^
The geometric mean concentrations of some compounds (particularly carbon
tetrachloride, p-dichlorobenzene, dichlorodifluoromethane, and trichlorofluoromethane)
are nearly uniform across the 12 UATMP monitoring locations, while the geometric mean
concentrations for most other compounds exhibit significant spatial variations.
The profiles of geometric mean concentrations of the program-wide prevalent
hydrocarbons (Figure 4-1) are nearly identical across all monitoring stations, with
relatively higher concentrations consistently occurring at the El Paso, Texas, and
Burlington, Vermont, monitoring stations and with the lowest concentrations consistently
occurring at the Underbill, Vermont, and Beulah, North Dakota, monitoring stations.
The geometric mean concentration profiles for the program-wide prevalent polar
compounds (Figure 4-3) exhibit dramatic differences. Acetonitrile is present in relatively
high concentrations at only one monitoring location (Baton Rouge, Louisiana) and at or
near the detection limit at the remaining 11 monitoring locations. Methyl terf-butyl ether
is present in relatively high concentrations at only one site (Camden, New Jersey), at
moderate concentrations at three other locations, and at or near the detection limit at the
remaining monitoring sites. Methyl ethyl ketone was reported from the Beulah, North
Dakota monitoring location due to sampler contamination.
The geometric mean concentrations of many compounds varied significantly, even among
stations located in close proximity (e.g., Burlington, Brattleboro, Rutland, and Underbill;
Baton Rouge, Garyville, and Hahnville).
4-4
-------
4.1.4 Variability
Table 4-2 lists, for each monitoring location, the three program-wide prevalent
compounds with lowest coefficients of variation and the three program-wide prevalent
compounds with highest. Only program-wide prevalent compounds are considered in this table
because nondetect observations strongly influence variability. As with the trends in central
tendency, the trends in variability vary from one site to the next, but some general trends are
apparent:
Ambient air concentrations of dichlorodifluoromethane, carbon tetrachloride, and
chloromethane had very low variability at most of the monitoring locations.
Concentrations of acetonitrile, toluene, and methylene chloride consistently varied greatly
during the 1998 UATMP.
4.2 Data Summary Parameters for Carbonyls
Using the same four data summary parameters discussed in Section 4.1, the tables in
Appendix E provide an overview of the carbonyl monitoring results from the 1998 UATMP. The
raw monitoring data are included in Appendix G. The following paragraphs review the basic
findings indicated by the carbonyl data summary tables.
4.2.1 Prevalence
Like the VOCs, prevalence of carbonyls in ambient air varied significantly from compound
to compound and from monitoring location to monitoring location. With the exceptions of
2,5-dimethylbenzaldehyde, crotonaldehyde, and isovaleraldehyde, the carbonyls were generally
present at a prevalence greater than 75 percent at all of the monitoring locations. For the
purposes of this report, program-wide prevalent carbonyl compounds were identified. In the
1998 UATMP, the program-wide prevalent carbonyls are acetaldehyde, acetone,
butyl/isobutyaldehyde, and formaldehyde. As noted in Section 2.5.2, the carbonyl sampling and
analytical method cannot separate butyraldehyde and isobutryaldehyde, and instead reports the
4-5
-------
sum of the concentrations for these two compounds, rather than reporting separate concentrations
for each compound.
Readers interested in examining ambient air levels of less program-wide prevalent carbonyl
compounds should refer to the raw monitoring data in Appendix G and the data interpretation
methodologies in Section 8.
4.2.2 Concentration Range
Table 4-3 summarizes the highest concentrations of carbonyls measured during the 1998
UATMP. Like the VOCs, most carbonyls (greater than 75 percent) had concentration peaks of
less than 1 ppbv. Specific trends identified include:
At 11 of the 12 monitoring sites, acetone and acetaldehyde had peak concentrations
greater than 1 ppbv.
Formaldehyde had peaks greater than 1 ppbv at all of the monitoring stations and peaks
greater than 5 ppbv at 6 of the 12 monitoring stations.
4.2.3 Central Tendency
Figure 4-4 illustrates how central tendency concentrations of the program-wide prevalent
carbonyl compounds varied among the 1998 UATMP monitoring locations. Like the spatial
variations shown for VOC central tendency concentrations, the spatial variations for carbonyl
central tendency concentrations differ for each compound. Nonetheless, some general trends are
apparent:
The profiles of central tendency concentrations illustrate that the highest concentrations
typically occurred at Camden, New Jersey, and El Paso, Texas. This tendency of high
concentrations of the compounds of interest in the samples from the El Paso monitoring
site is also seen in the VOCs.
No strong central tendency of low concentrations at a particular monitoring site is seen in
the figure.
4-6
-------
4.2.4 Variability
Along with the VOCs, Table 4-2 lists, for each monitoring location, the three compounds
with lowest coefficients of variation and the three with highest. Butyr/isobutyraldehyde is among
the least variable, while acetaldehyde is among the most variable, but these variability trends for
the carbonyl data are not as strong as those for the VOC data.
«> « t. x*» "~ ^ * \ v i ^V X ^6. *" \ *"
^Jjjfen interpreting fM^f|» A^ma^jp^flwefiew^
.n&tolwnjffa^fomost ^ "
the most program-^vide prevalent compounds in urban air pollution.
J^r^am^H^^e^alent in,urban air ar&noi con^^jifedmtkis report. Furth^r,^f:^ *" ^^
'nftrtif'i-nntrnn fitranfiot- fhmilil intomrat meniro-foro-nf>o
spatial variations" in proper
urban settings in the United States.
4-7
-------
Figure 4-1
Geometric Mean Concentrations of the Program-Wide Prevalent Hydrocarbons,
by Monitoring Location, by Compound
ACETYLENE
.S
II3
8 I 2
X 1
Si1
Monitoring Location
BENZENE
1.4
1.2
= 1
|| 0.8
S £ 0.6
0.4
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gm
Monitoring Location
0.5 •
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8s 0.2
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ETHYL
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ffl CO
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PROPYLENE
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a l
CD co
ffi O
Monitoring Location
Note: These figures are presented in different scales and show the numerical value of the highest geometric mean
concentration calculated for the 1998 UATMP sites.
4-8
-------
Figure 4-1 (Continued)
Geometric Mean Concentrations of the Program-Wide Prevalent Hydrocarbons,
by Monitoring Location, by Compound
entrati
ppbv)
o
in
TOLUENE
2.5 T-
Monitoring Location
1.4 -I
no
S f no
g & 0.6
g -" 0.5
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m,p-XYLENE
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Monitoring Location
0.75 !
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§ S 0.3
3 0.15
o-XYLENE
I
Monitoring Location
Note: These figures are presented in different scales and show the numerical value of the highest geometric mean
concentration calculated for the 1998 UATMP sites.
4-9
-------
Figure 4-2
Geometric Mean Concentrations of the Program-Wide Prevalent Halogenated
Hydrocarbons, by Monitoring Location, by Compound
CARBON TETRACHLORIDE
0.1
0.08
0.06
1|
S a 0.04
o
u
0.02
0.094
OC
ca
a.
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Monitoring Location
CHLOROM ETHANE
Monitoring Location
p-DICHLOROBENZENE
g 0.08 -
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at 9; n 04
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Monitoring Location
Note: These figures are presented in different scales and show the numerical value of the highest geometric mean
concentration calculated for the 1998 UATMP sites.
4-10
-------
Figure 4-2 (Continued)
Geometric Mean Concentrations of the Program-Wide Prevalent Halogenated
Hydrocarbons, by Monitoring Location, by Compound
0.75 i
I °'6
1 f 0-45
8 & °-3 '
J 0.15.
DICHLORODIFLUOROM ETHANE
£
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8 S
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0.6
0.5
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0
METHYLENE CHLORIDE
a
5
§
cc
oc
Monitoring Location
O 0 1 R -
2 *>
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c 005-
o
TETRACHLOROETHYLENE
041* I
Monitoring Location
Note: These figures are presented in different scales and show the numerical value of the highest geometric mean
concentration calculated for the 1998 UATMP sites.
4-11
-------
Figure 4-2 (Continued)
Geometric Mean Concentrations of the Program-Wide Prevalent Halogenated
Hydrocarbons, by Monitoring Location, by Compound
0.2
| 0.15
| f °^
§ ~ 0-05
o
0
1,1,1-TRICHLOROETHANE
Monitoring Location
D
CC
0.4
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§t
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0.2
TRICHLOROFLUOROM ETHANE
,
Monitoring Location
' V
'
1* *
•
CC
DC
oncentration
(ppbv)
o o
b P '-> P
CJ1 -+ U1 fO
0.158
TRICHLOROTRIFLUOROETHANE
Monitoring Location
Note: These figures are presented in different scales and show the numerical value of the highest geometric mean
concentration calculated for the 1998 UATMP sites.
4-12
-------
Figure 4-3
Geometric Mean Concentrations of the Program-Wide Prevalent Polar Compounds
by Monitoring Location, by Compound
Concentration
(ppbv)
7
6
5
4
3
2
1
0
ACETONITRILE
6.78
CO
Monitoring Location
METHYL ETHYL KETONE
Monitoring Location
0.8
0.6
0.4
0.2
METHYL TEHT-BUTYL ETHER
Monitoring Location
Note: These figures are presented in different scales and show the numerical value of the highest geometric mean
concentration calculated for the 1998 UATMP sites.
4-13
-------
Figure 4-4
Geometric Mean Concentrations of the Program-Wide Prevalent Carbonyls,
by Monitoring Location, by Compound
.0 < 5 .
Hi-
o S.
o -S
c 05
o u-a
o
ACETALDEHYDE
CM
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ID
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° 0.1
ACETONE
?> f,T(i
Monitoring Station
BUTYR/ISOBUTYRALDEHYDE
0.51
.'i-iRISS
Monitoring Station
FORMALDEHYDE
Monitoring Station
Note: These figures are presented in different scales and show the numerical value of the highest geometric mean
concentration calculated for the 1998 UATMP sites.
4-14
-------
Table 4-1
Summary of Highest VOC Concentrations
Number of Monitoring Stations With Highest Concentration in Listed Range
Chemical
Samples
with
Cone.
>DL
Number of Stations
Concentration
<1 ppbv
Concentration a 1
but <5 ppbv
Concentration ^5
but <10 ppbv
Concentration
2 10 ppbv
lydrocarbons
Acetylene
lenzene
,3-Butadiene
Cthylbenzene
i-Octane
'ropylene
Styrene
Toluene
,2,4-Trimethylbenzene
,3,5-Trimethylbenzene
n-,/?-Xylene
9-Xylene
322
322
188
311
270
322
217
322
317
263
320
320
0
3
11
10
12
2
8
0
9
11
4
10
7
9
1
1
0
7
4
6
2
1
7
1
4
0
0
0
0
2
0
4
1
0
0
0
1
0
0
1
0
1
0
2
0
0
1
1
lalogenated Hydrocarbons
iromochloromethane
Jromodichloromethane
Jromoform
Bromomethane
Carbon Tetrachloride
Chlorobenzene
Chloroethane
Chloroform
Chloromethane
Chloromethylbenzene
Chloroprene
Dibromochloromethane
1,2-Dibromoethane
-n-Dichlorobenzene
o-Dichlorobenzene
'-Dichlorobenzene
0
0
0
25
309
2
11
27
321
0
9
0
1
4
3
30
12
12
12
12
12
12
12
12
6
12
10
12
12
12
12
12
0
0
0
0
0
0
0
0
5
0
2
0
0
0
0
0
0
0
0
0
0
0
0
0
1
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
4-15
-------
Table 4-1 (Continued)
Summary of Highest VOC Concentrations
Number of Monitoring Stations With Highest Concentration in Listed Range
Chemical
Samples
with
Cone.
>DL
Number of Stations
Concentration
<1 ppbv
Concentration z 1
but <5 ppbv
Concentration ^5
but <10 ppbv
Concentration
2:10 ppbv
lalogenated Hydrocarbons (Continued)
1,1-Dichloroethane
,2-Dichloroethane
,1-Dichloroethene
ds- 1 ,2-Dichloroethylene
trans- 1 ,2-Dichloroethylene
,2-Dichloropropane
cis- 1 ,3-Dichloropropene
trans- 1 ,3-Dichloropropene
)ichlorodifluoromethane
)ichlorotetrafluoroethane
lexachloro-l,3-Butadiene
Vlethylene Chloride
, 1 ,2,2-Tetrachloroethane
Petrachloroethylene
,2,4-Trichlorobenzene
.,1,1 -Trichloroethane
, 1 ,2-Trichloroethane
Frichloroethylene
rrichlorofluoromethane
Prichlorotrifluoroethane
Vinyl Chloride
1
5
3
1
0
0
0
0
322
14
3
269
3
64
5
314
1
20
321
321
5
12
12
12
12
12
12
12
12
7
12
12
5
12
10
12
11
12
12
8
12
12
0
0
0
0
0
0
0
0
5
0
0
6
0
2
0
0
0
0
4
0
0
0
0
0
0
0
0
0
0
0
0
0
1
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
1
0
0
0
0
0
tolar Compounds
Acetonitrile
Acrylonitrile
Ethyl Aery late
Ethyl fert-Butyl Ethel-
Methyl Ethyl Ketone*
Methyl Isobutyl Ketone
Methyl Methacrylate
Methyl tert-Butyl Ether
tert-Amyl Methyl Ether
100
50
4
0
287
64
6
164
22
0
7
12
12
0
12
12
9
11
2
5
0
0
11
0
0
2
1
3
0
0
0
0
0
0
1
0
7
0
0
0
0
0
0
0
0
* Methyl Ethyl Ketone was not reported at the Beulah, ND, site due to sampler contamination problems.
4-16
-------
Table 4-2
Compounds With Highest and Lowest Coefficients of Variation, by Monitoring Location
Monitoring
Location
Three Compounds With Highest Coefficients
of Variation (Value)
Three Compounds With Lowest Coefficients
of Variation (Value)
B2LA
Methyl rerr-Butyl Ether (1.33)
Toluene (1.14)
Ethylbenzene (0.99)
Carbon Tetrachloride (0.27)
p-Dichlorobenzene (0.16)
Dichlorodifluoromethane (0.14)
BRVT
Acetonitrile (2.89)
Toluene (1.10)
Trichlorotrifluoroethane (1.04)
1,1,1 -Trichloroethane (0.19)
Chloromethane(0.15)
p-Dichlorobenzene (0.09)
BUND
Acetonitrile (1.07)
Butyr/Isobutyraldehyde (1.03)
Tetrachloroethylene (0.99)
Carbon Tetrachloride (0.21.)
Chloromethane(O.lO)
p-Dichlorobenzene (0.10)
BUVT
Acetonitrile (3.51)
Methylene Chloride (1.46)
MethyI Ethyl Ketone (1.11)
1,1,1 -Trichloroethane (0.15)
Chloromethane (0.14)
Dichlorodifluoromethane (0.14)
CANJ
Acetonitrile (1.82)
Propylene (0.90)
Methylene Chloride (0.58)
Carbon Tetrachloride (0.24)
Trichlorotrifluoroethane (0.24)
Dichlorodifluoromethane (0.20)
EPTX
m-,p-Xylene (3.97)
o-Xylene(3.91)
Ethylbenzene (3.65)
Carbon Tetrachloride (0.31)
Chloromethane (0.28)
Trichlorotrifluoroethane (0.27)
GALA
,1,1 -Trichloroethane (4.09)
Acetonitrile (2.79)
Propylene (2.32)
Acetaldehyde(0.31)
Carbon Tetrachloride (0.26)
p-Dichlorobenzene (0.20)
Note: As the summary tables in Appendix D show, compounds with low prevalence also have low variability,
because a large fraction of the sampling results (i.e., the nondetects) have the exact same value: one-half
the detection limit. Therefore, the summary of coefficients of variation in this table only considers the
compounds identified as prevalent for the 1998 UATMP (see Sections 4.1.1 abd 4.2.1 for these lists).
4-17
-------
Table 4-2 (Continued)
Compounds With Highest and Lowest Coefficients of Variation, by Monitoring Location
Monitoring
Location
Three Compounds With Highest Coefficients
of Variation (Value)
Three Compounds With Lowest Coefficients
of Variation (Value)
GREY
Toluene (1.64)
Acetonitrile(1.40)
Butyr/isobutyraldehyde (1.09)
Trichlorotrifluoroethane (0.11)
Dichlorodifluoromethane (0.08)
p-Dichlorobenzene (<0.01)
HALA
Acetonitrile (3.92)
Methyl ren-Butyl Ether (3.16)
Tetrachloroethylene (2.22)
Trichlorotrifluoroethane (0.31)
Carbon Tetrachloride (0.18)
Dichlorodifluoromethane (0.12)
PARR
Methylene Chloride (1.76)
Acetonitrile (1.47)
Butyr/isobutyraldehyde (1.09)
1,1,1 -Trichloroethane (0.21)
p-Dichlorobenzene (0.18)
Dichlorodifluoromethane (0.17)
RUVT
Acetonitrile (2.88)
Methylene Chloride (1.03)
Butyr/isobutyraldehyde (0.68)
Trichlorotrifluoroethane (0.17)
1,1,1-Trichloroethane (0.17)
Chloromethane(0.15)
UNVT
Acetonitrile (2.46)
Methylene Chloride (1.69)
Toluene (1.24)
Tetrachloroethylene (0.20)
Chloromethane(0.17)
Dichlorodifluoromethane (0.11)
Notes: As the summary tables in Appendix D show, compounds with low prevalence also have low variability,
because a large fraction of the sampling results (i.e., the nondetects) have the exact same value: one-half
the detection limit. Therefore, the summary of coefficients of variation in this table only considers the
compounds identified as prevalent for the 1998 UATMP (see Sections 4.1.1 and 4.2.1 for these lists).
4-18
-------
Table 4-3
Summary of Highest Carbonyl Concentrations
Number of Monitoring Stations With Highest Concentration in Listed Range
Chemical
Acetaldehyde
Acetone
Acrolein
Jenzaldehyde
Butyr/Isobutyraldehyde
Crotonaldehyde
2,5-Dimethylbenzaldehyde
formaldehyde
lexaldehyde
sovaleraldehyde
'ropionaldehyde
folualdehydes
Valeraldehyde
Samples
with
Cone.
>DL
315
314
220
307
309
142
48
315
311
186
314
270
305
Number of Stations
Concentration
-------
5.0 Data Interpretation: Hydrocarbons
Hydrocarbons are organic compounds that contain only carbon and hydrogen. The
hydrocarbons are derived mostly from crude petroleum and also from coal tar and plant sources
and are classified according to the arrangement of the atoms, as alicyclic, aliphatic, and aromatic.
Hydrocarbons are of prime economic importance because they encompass the constituents of the
major fossil fuels, petroleum and natural gas, as well as plastics, waxes, and oils. In urban air
pollution, these components—along with oxides of nitrogen (NOX) and sunlight—contribute to the
formation of tropospheric ozone.
As stated above, hydrocarbons in the atmosphere originate from natural sources and from
various anthropogenic sources, such as combustion of fuel and biomass, petroleum refining,
petrochemical manufacturing, solvent use, and gas and oil production and use. Studies have
shown that emissions from different anthropogenic sources vary significantly from location to
location. For example, on a nationwide basis, EPA estimates that 50 percent of anthropogenic
nonmethane volatile organic compound releases in 1996 came from industrial processes,
42 percent from transportation, 6 percent from fuel combustion, and the rest from other sources
(USEPA, 1997). In urban areas, however, the estimated contributions of different source
categories differ from these national averages. For instance, a 1987 study in the Los Angeles
area estimated that 49 percent of nonmethane hydrocarbon emissions come from vehicle exhaust,
11 percent from liquid gasoline, 10 percent from gasoline vapor, and 30 percent from sources
other than motor vehicles (Fujita et al., 1994). These figures suggest that motor vehicles may
play a greater role in hydrocarbon emissions in urban areas than national statistics indicate.
As noted in Section 2, the sampling and analytical methods used in the 1998 UATMP
measure concentrations of 12 hydrocarbons, all of which have fewer than ten carbon atoms.
These 12 hydrocarbons tend to be gases or volatile liquids under standard atmospheric conditions
and are commonly referred to as VOCs. The discussions in this chapter center on the general
trends observed for 7 program-wide prevalent hydrocarbons and consider hydrocarbon
concentrations quantified at the 12 monitoring locations, with respect to:
5-1
-------
Correlations between concentrations of the program-wide prevalent hydrocarbons and
concentrations of other compounds measured at the same time at the same monitoring
location;
Correlations between concentrations of the program-wide prevalent hydrocarbons and
temperature;
Correlations between concentrations of the program-wide prevalent hydrocarbons and
meteorological parameters.
Temporal (annual) variations in hydrocarbon concentrations measured during the 1994
through 1998 UATMPs;
Spatial variations in hydrocarbon concentrations measured during the 1998 UATMP;
Relationship between spatial variations in hydrocarbon concentrations measured during
the 1998 UATMP and estimates of motor vehicle emissions; and
Relationship between spatial variations in hydrocarbon concentrations measured during
the 1998 UATMP and estimates of industrial emissions.
trends and patterns in the UATMP data, such detailed analyses were not-included in the
'*• Viti^ £ -iu ^ "" ~5?<^ (, ,-x , ' * * * *
scope of tmsMvork. " •<*-*'«; <• < a
*» * •»*» n- '.. •, f -y> •> c""•«.*.!* J1 *" ^ *••>s ^ > gJ
5.1 Correlations Between Concentrations of Different Compounds
From the ambient air monitoring data collected for each sampling event at each site,
Pearson correlation coefficients were calculated to compare concentrations of the program-wide
prevalent compounds from the four groups of chemicals studied in the 1998 UATMP
(i.e., hydrocarbons, halogenated hydrocarbons, polar compounds, and carbonyls). The following
discussion summarizes the calculated correlations.
5-2
-------
5.1.1 Correlations Between Halogenated Hydrocarbons and Hydrocarbons
Figure 5-1 shows the distribution of Pearson correlation coefficients calculated from the
ambient air monitoring data for the program-wide prevalent halogenated hydrocarbons and
program-wide prevalent hydrocarbons.
As the distribution of Pearson correlation coefficients in Figure 5-1 shows, ambient air
concentrations of the program-wide prevalent halogenated hydrocarbons measured during the
1998 UATMP were weakly correlated with ambient air concentrations of the program-wide
prevalent hydrocarbons. Approximately 25 percent of the correlation coefficients were between
+0.50 and +0.75, indicating a moderate positive correlation. Nearly 42 percent of the correlation
coefficients were between -0.25 and +0.25, indicating very weak or no correlation. However, the
average correlation is statistically significant (0.250 ± 0.174) across the 12 sites. These weak
correlations generally suggest that the factors that most strongly affect levels of halogenated
hydrocarbons in ambient air are different from the factors that affect ambient air concentrations
of hydrocarbons.
5.1.2 Correlations Between Hydrocarbons and Polar Compounds
Figure 5-1 shows the distribution of Pearson correlation coefficients calculated from the
ambient air monitoring data for the program-wide prevalent hydrocarbons and program-wide
prevalent polar compounds.
As the distribution of Pearson correlation coefficients in Figure 5-1 shows, ambient air
concentrations of the program-wide prevalent hydrocarbons measured during the 1998 UATMP
were very weakly correlated with ambient air concentrations of the program-wide prevalent polar
compounds. Approximately 16 percent of the correlation coefficients were between +0.50 and
+0.75, indicating a moderate positive correlation. Nearly 58 percent of the correlation
coefficients were between -0.25 and +0.25, indicating very weak or no correlation. However, the
average correlation was statistically significant across the 12 sites (0.199 ± 0.152). These weak
correlations generally suggest that the factors that most strongly affect levels of hydrocarbons in
5-3
-------
ambient air are different from the factors that affect ambient air concentrations of polar
compounds.
5.1.3 Correlations Between Carbonyls and Hydrocarbons
Figure 5-1 shows the distribution of Pearson correlation coefficients calculated from the
ambient air monitoring data for the program-wide prevalent carbonyls and program-wide
prevalent hydrocarbons.
The distribution of Pearson correlation coefficients in Figure 5-1 shows that ambient air
concentrations of the program-wide prevalent hydrocarbons measured during the 1998 UATMP
were weakly correlated with ambient air concentrations of the program-wide prevalent carbonyls.
Approximately 17 percent of the correlation coefficients were between +0.50 and +0.75,
indicating a moderate positive correlation. Less than 50 percent of the correlation coefficients
were between -0.25 and +0.25, indicating very weak or no correlation. The average correlation
was not statistically significant across the 12 sites (0.160 ± 0.175). These weak correlations
generally suggest that the factors that most strongly affect levels of hydrocarbons in ambient air
are from the factors that affect ambient air concentrations of carbonyl compounds.
5.2 Correlations Between Concentrations and Temperature
5.2.1 Temperature
According to Table 5-1, the program-wide prevalent hydrocarbons generally had negative
correlations with maximum, minimum, and average temperature across all 12 sites. This type of
correlation would suggest that increasing temperature would relate to decreasing measured
concentration of hydrocarbons. The Brattleboro, VT, site had the strongest negative correlation
of hydrocarbon concentration for all three temperature parameters (-0.476, -0.549, and -0.554,
respectively). The highest positive correlations of hydrocarbon concentration with these
meteorological parameters occurred at the Beulah, ND, site (0.318 and 0.134, respectively) while
the Little Rock site had the highest correlation with average temperature (0.228).
5-4
-------
Seasonal changes in daily average tern^erature are muck greater at the monitoring locations
^ih the nprth'thart atfhe monitoring locations in 1he south.^ These
-------
5.2.3 Dew Point Temperature and Visibility
According to Table 5-1, the program-wide prevalent hydrocarbons had a negative
correlation with the dew point temperature. The strongest negative correlation occurred at the
Burlington, VT, site (-0.471). The highest positive correlation of hydrocarbon concentration with
dew point temperature occurred at the Beulah, ND site (0.186). Visibility also had a negative
correlation with the program-wide prevalent hydrocarbons (-0.158 ± 0.106). The strongest
negative correlation occurred at the Baton Rouge, LA, site (-0.4762), while the highest positive
correlation occurred at the El Paso, TX, site (0.108).
Statistical significance of the correlation between the dew point temperature and visibility
with the measured hydrocarbon concentrations at the 95 percent confidence interval was also
calculated across all 12 sites. As Table 5-1 shows, only the visibility parameter was statistically
significant, suggesting that as the visibility decreases (or haziness increases), the ambient
concentrations of hydrocarbons decrease.
5.3 Annual Variations
Table 5-2 presents average concentrations of program-wide prevalent hydrocarbons at
each of the 12 monitoring stations for the 1994 through 1998 UATMPs. In very few cases are
consistent positive or negative trends seen for the concentration of a specific hydrocarbon
compound across the entire 4 year period (e.g., an annual decrease in the concentration of a
compound in each year). Readers should note that changes in concentrations can result from
shifting prevailing winds and might not necessarily indicate increases or decreases in emissions.
In general, concentrations of total program-wide prevalent hydrocarbons have decreased annually
since 1995.
5-6
-------
5.4 Spatial Variations
To provide a sense of how overall levels of hydrocarbons varied among the UATMP
monitoring locations, Figure 5-2 compares the geometric means of the sums of the program-wide
prevalent hydrocarbon concentrations for each monitoring location. These data are provided for
comparison purposes only and should not be confused with concentrations of total nonmethane
organic compounds, which is another common air quality measurement.
Figure 5-2 clearly indicates that levels of the program-wide prevalent hydrocarbons at El
Paso, Texas (EPTX), were significantly higher than the levels measured at any of the other
monitoring stations. The figure also indicates that levels of the most program-wide prevalent
hydrocarbons were lowest at Underbill, Vermont (UNVT), and Beulah, North Dakota (BUND).
5.5 The Impact of Motor Vehicle Emissions on Spatial Variations
Motor vehicles significantly contribute to air pollution in urban environments. Pollutants
found in motor vehicle exhaust generally result from incomplete combustion of vehicle fuels.
Although modern vehicles and, more recently, vehicle fuels have been engineered to minimize air
emissions, all motor vehicles with internal combustion engines emit a wide range of chemical
pollutants. The magnitude of these emissions in urban areas primarily depends on the volume of
traffic, while the chemical profile of these emissions depends more on vehicle design and fuel
content. This report uses two parameters to evaluate the impact of motor vehicle emissions on
ambient air quality:
5-7
-------
Car ownership data; and
Motor vehicle emissions profiles.
5.5.1 Car Ownership Data
As an indicator of motor vehicle emissions near the UATMP monitoring locations,
Table 5-3 presents estimates of the number of cars owned by residents within 10 miles of each
monitoring location. The total number of cars owned within a 10-mile radius was estimated
based on a ratio of 0.74 cars per person (U.S. population of 260,000,000 and total number of cars
in U.S. of 193,400,0000).
For purposes of comparison, both car ownership data and the observed levels of total
program-wide prevalent hydrocarbons are presented in Table 5-3, ranked in descending order.
The data in the table indicate a positive linear correlation between car ownership data and
ambient air concentrations of hydrocarbons. However, readers should keep in mind other factors
that might impact the reliability of car ownership data as an indicator of ambient air monitoring
data results:
Estimates of higher car ownership within a 10-mile radius do not necessarily imply
increased motor vehicle use in the immediate vicinity of a monitoring location.
Conversely, sparsely populated regions often contain heavily traveled roadways.
Emissions sources in the area other than motor vehicles may significantly affect levels of
hydrocarbons in the ambient air.
5.5.2 Motor Vehicles Emissions Profiles
The magnitude of emissions from motor vehicles generally depends on the volume of
traffic in urban areas, but the composition of these emissions depends more on vehicle design.
Because the distribution of vehicle design (i.e., the relative number of cars of different styles) is
probably quite similar from one urban area to the next, the composition of air pollution resulting
from motor vehicle emissions is not expected to exhibit significant spatial variations. In support
5-8
-------
of this hypothesis, previous air monitoring studies have observed relatively constant
compositions of ambient air samples collected along heavily traveled urban roadways (Conner
et al., 1995). Roadside studies have found particularly consistent proportions of four
hydrocarbons (benzene, toluene, ethylbenzene, and the xylene isomers - the "BTEX"
compounds) both in motor vehicle exhaust and in ambient air near roadways.
To examine the impact of motor vehicle emissions on air quality at the 1998 UATMP
monitoring sites, Figure 5-3 compares concentration ratios for the BTEX compounds measured
during the 1998 UATMP to the ratios reported in a roadside study (Conner et al., 1995). This
comparison provides a qualitative depiction of how greatly motor vehicle emissions affect air
quality at the UATMP monitoring locations: the more similar the concentration ratios at a
particular monitoring location are to those of the roadside study, the more likely that motor
vehicle emissions impact ambient levels of hydrocarbons at that location.
As Figure 5-3 shows, the concentration ratios for BTEX compounds measured at every
UATMP monitoring station bear some resemblance to the ratios reported in the roadside study.
The BTEX ratio for the Baton Rouge monitoring location is most similar to the roadside study
profile. For all monitoring locations except El Paso, Texas, the toluene:ethylbenzene ratio is
clearly the largest value of the four ratios and the xylene:ethylbenzene ratio is clearly the smallest
value of the ratios. This observation suggests, though certainly does not prove, that emissions
from motor vehicles significantly affect levels of hydrocarbons in urban ambient air. It should be
noted that BTEX concentration ratios for El Paso, Texas deviate from the roadside study profile.
This deviation indicates that emissions from sources other than motor vehicles in these locations
may have a strong influence on local air quality.
5.6 The Impact of Industrial Emissions on Spatial Variations
For purposes of comparison, Table 5-3 summarizes emissions data for each monitoring
location, and ranks each data set with the highest value assigned the rank of one. For each
monitoring location, Table 5-3 includes:
5-9
-------
• The geometric mean of the sum of the program-wide prevalent hydrocarbon
concentrations for each sampling event.
• The sum of emissions of 6 of the 7 program-wide prevalent hydrocarbons detected during
the 1998 UATMP reported to TRI in 1997 by facilities within 10 miles of the 1998
UATMP monitoring locations. The table does not account for emissions of acetylene
because industries are not required to disclose releases of this compound to TRI.
Total emissions reported to TRI in 1997 by facilities within 10 miles of the 1998 UATMP
monitoring locations.
As the table shows, the TRI emissions ranks for the 12 sites were not entirely consistent
with the respective rank of the total ambient air concentration of the program-wide prevalent
hydrocarbons. For instance:
• The Baton Rouge, LA, monitoring site had high concentrations of program-wide
prevalent hydrocarbons, high emissions of program-wide prevalent hydrocarbons reported
to TRI, and high emissions of total hydrocarbons reported to TRI.
• Some monitoring locations (e.g., Burlington and Rutland, VT and El Paso, TX) had
relatively high concentrations of the program-wide prevalent hydrocarbons, but had
relatively low levels of both program-wide prevalent hydrocarbon and total industrial
emissions reported to TRI.
• Other monitoring locations (e.g., Hahnville and Garyville, LA) had relatively low
concentrations of hydrocarbons, but had relatively high levels of emissions reported to
TRI.
To examine the TRI emissions data more closely, Table 5-4 compares the reported air
releases for the individual program-wide prevalent hydrocarbons (excluding acetylene) to the
corresponding geometric mean concentrations measured during the 1998 UATMP. For ease of
interpretation, Table 5-4 lists the monitoring locations in order of decreasing geometric mean
concentration for each compound. Readers should keep in mind that the concentrations of these
compounds are quite low in all cases, 0.20 to 3 ppbv, and conclusions regarding spatial variation
should be made cautiously.
5-10
-------
The El Paso, TX, monitoring site reported the highest concentrations for all three of the
hydrocarbon compounds presented in Table 5-4. However, low to moderate levels of these
compounds are reported to TRI by facilities within 10 miles of the facilities. The Texarkana,
AR, Beulah, ND, and Underhill, VT, sites consistently reported low pollutant concentrations and
no program-wide prevalent hydrocarbon emissions were reported to TRI by facilities with 10
miles of these sites.
5-11
-------
Figure 5-1
Summary of Data Correlations Between Groups of Compounds
35
30
25
VI
O>
520
O
§ 15
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LL
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5
0
Correlations BehneenHdogenatedHyaVocabons crd Hydrocarbons
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5-12
-------
Figure 5-2
Geometric Mean of the Daily Concentration of the Prevalent Hydrocarbons
re
Q
14
12
EU10
3 O.
',.•>-<'•
* -*
"_ i »*
•(""*!»
•' s • *'r^
U^sC; -; •$;•*
^
ffTX B2LA BUVT RUVT HALA PARR CAMJ BRVT
Monitoring Location
GALA
GRET
BUND
UNVT
-------
Figure 5-3
Comparison of 1998 UATMP BTEX Concentration Profiles to Conner et al. (1995) Profiles
Roadside
B2LA
BR VT
M o n ito rln g S la tlo n
BUND
B U VT
| DB enzene-Elhylbenzene •Toluene-Elhylbenzene Elm p xylene-elhylbenzene C3o xylene - elhylbenzene
-------
Figure 5-3 (Continued)
Comparison of 1998 UATMP BTEX Concentration Profiles to Conner et al. (1995) Profiles
R oadside
C AN J
EP TX
M on ito rin g Static n
GREY
JOB e n ze n e • E th y Ib e n ze n e •! o In e n e-E th ylbenze ne Dm p xyle n e -ethylbe n ze n e Do xylene - ethylbenzene
-------
Figure 5-3 (Continued)
Comparison of 1998 UATMP BTEX Concentration Profiles to Conner et al. (1995) Profiles
o\
Roadside
H ALA
PARR
M o n Itoring S talio n
R U VT
U N VT
|PB e nze ne-E Ih ylbe nze ne •! o lue n e -E thylbe nze ne Gm p xylen e-ethylbe nze ne Do xylene - ethylbenzene
-------
Table 5-1
Summary of Pearson Correlations for Selected Meteorological Parameters and Measured Hydrocarbon Concentrations
Meteorological Parameter
Maximum Temperature
Minimum Temperature
Average Temperature
Wind Speed*
Sea level pressure
Dew Point Temperature
Visibility*
Average Correlation
-0.040 ±0.1 36
-0.119±0.126
-0.088 ±0.1 34
-0.254 ±0.1 30
0.020 + 0.103
-0.057 ±0.1 12
-0.158 ±0.106
Highest Positive
Correlation Site (Value)
Beulah, ND
(0.318)
Beulah, ND
(0.134)
Little Rock, AR
(0.222)
Hahnville, LA
(0.140)
Texarkana, AR
(0.267)
Beulah, ND
(0.186)
El Paso, TX
(0.103)
Strongest Negative
Correlation Site (Value)
Brattleboro, VT
(-0.476)
Brattleboro, VT
(-0.549)
Brattleboro, VT
(-0.554)
Little Rock, AR
(-0.6347)
Beulah, ND
(-0.277)
Burlington, VT
(-0.471)
Baton Rouge, LA
(-0.4762)
Statistically significant across the 12 sites.
-------
Table 5-2
Average Concentrations (ppbv) of Program-Wide Prevalent Hydrocarbons for the
1998 UATMP Compared to the Same Compounds for Previous Years
1994
1995
1996
1997
1998
B2LA
Acetylene
Benzene
Ethylbenzene
m-.p-Xylene
o-Xylene
Propylene
Toluene
3.50
0.60
0.18
0.78
0.31
1.84
1.14
1.92
0.67
0.22
0.63
0.32
1.39
1.19
1.80
0.59
0.26
0.71
0.35
1.30
0.99
1.97
0.77
0.39
1.03
0.58
1.77
2.02
BRVT !
Acetylene " -
Benzene
Ethylbenzene
m-,/?-Xylene
o-Xylene
Propylene
Toluene
1.24
0.30
0.15
0.47
0.16
0.60
1.34
2.45
0.55
0.20
0.60
0.24
0.90
1.26
1.52
0.52
0.17
0.47
0.24
0.79
1.04
1.66
0.58
0.19
0.46
0.24
0.84
1.30
BUND
Acetylene
Benzene
Ethylbenzene
m-,/?-Xylene
o-Xylene
Propylene
Toluene
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.62
0.26
0.09
0.17
0.09
0.35
0.45
BUVT ;
Acetylene
Benzene
Ethylbenzene
m-,p-Xylene
o-Xylene
Propylene
Toluene
4.80
0.66
0.26
1.08
0.43
1.31
1.52
3.29
0.79
0.29
0.86
0.40
1.12
1.59
2.84
0.92
0.35
1.03
0.51
1.27
1.87
2.38
0.86
0.31
0.84
0.42
1.22
1.85
CANJ
Acetylene 5.69
Benzene 0.57
Ethvlbenzene 0.29
3.62
0.69
0.17
3.22
0.65
0.20
2.22
0.67
0.20
1.75
0.58
0.17
Indicates compound was not included in the UATMP for that year.
5-18
-------
Table 5-2 (Continued)
Average Concentrations (ppbv) of Program-Wide Prevalent Hydrocarbons for the
1998 UATMP Compared to the Same Compounds for Previous Years
m-,/7-Xylene
o-Xylene
Propylene
Toluene
1994 1995
1.0 0.79
0.24 0.28
2.36 1.87
2.23 1.26
1996
0.67
0.29
1.74
1.47
1997
0.62
0.30
1.56
1.29
1998
0.44
0.22
1.22
1.08
EPTX
Acetylene
Benzene
Ethylbenzene
m-,p-Xylene
o-Xylene
Propylene
Toluene
9.90
1.28
0.47
1.89
- - 0.74
2.18
2.90
5.49
1.25
0.41
1.29
0.56
1.57
2.67
4.61
1.56
0.54
1.26
0.54
1.62
3.14
5.14
1.35
1.33
4.28
-1.97-
1.77
2.93
GALA •
Acetylene
Benzene
Ethylbenzene
m-,p-Xylene
o-Xylene
Propylene
Toluene
2.69
0.36
0.13
0.49
0.16
0.66
0.81
1.15
0.47
0.15
0.32
0.13
0.63
0.71
1.18
0.50
0.15
0.40
0.21
0.91
1.18
1.29
0.48
0.18
0.42
0.22
1.79
1.39
GREY j
Acetylene
Benzene
Ethylbenzene
m-,p-Xylene
o-Xylene
Propylene
Toluene
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.14
0.21
0.12
-
-
1.04
0.42
0.15
0.23
0.13
0.48
1.16
HALA
Acetylene
Benzene
Ethylbenzene
m-.p-Xylene
o-Xylene
Propylene
Toluene
1.41
0.48
0.20
0.84
0.33
0.92
5.73
1.25
0.62
0.11
0.34
0.14
1.26
0.77
0.98
0.50
0.15
0.40
0.20
1.52
0.90
1.49
0.77
0.32
0.46
0.23
1.70
1.50
Indicates compound was not included in the UATMP for that year.
5-19
-------
Table 5-2 (Continued)
Average Concentrations (ppbv) of Program-Wide Prevalent Hydrocarbons for the
1998 UATMP Compared to the Same Compounds for Previous Years
1994 1995
1996
1997
1998
PARR
Acetylene
Benzene
Ethylbenzene
m-.p-Xylene
o-Xylene
Propylene
Toluene
-
-
-
-
-
-
-
-
-
-
-
-
-
-
1.32
0.44
0.18
0.41
0.21
0.65
0.74
2.13
0.63
0.23
0.56
0.30
0.98
0.97
RUVT
Acetylene -
Benzene
Ethylbenzene
m-,p-Xylene
o-Xylene
Propylene
Toluene
4.41
0.51
0.27
0.94
0.36
0.83
1.55
2.60
0.66
0.24
0.74
0.33
0.91
1.40
- -2.25
0.75
0.28
0.80
0.40
1.05
1.71
2.15
0.68
0.27
0.72
0.36
0.96
1.69
UNVT . : : t
Acetylene
Benzene
Ethylbenzene
m-,p-Xylene
o-Xylene
Propylene
Toluene
0.82
0.13
0.27
0.18
0.09
0.08
0.33
0.85
0.24
0.08
0.21
0.11
0.23
0.36
0.58
0.21
0.06
0.10
0.06
0.26
0.24
0.62
0.22
0.07
0.12
0.07
0.26
0.36
• Indicates compound was not included in the UATMP for that year.
5-20
-------
Table 5-3
Ranking of Monitoring Stations by Levels of Total Program-Wide Prevalent Hydrocarbons
to
Monitoring
Location
B2LA
BRVT
BUND
BUVT
CANJ
EPTX
GALA
GREY
HALA
PARR
RUVT
UNVT
Geometric Means the of
Total Program- Wide
Prevalent Hydrocarbon
Concentrations3
ppbv
1998
7.65
4.72
1.88
7.61
5.00
12.87
4.07
3.01
5.36
5.07
6.28
1.59
Cone.
Rank
2
8
11
3
7
1
9
10
5
6
4
12
Industrial Emissions of
Program-Wide Prevalent
Hydrocarbons within a 10-
Mile Radius of the
Monitoring Location5
Pounds in
1997
527,478
14,586
0
12,768
190,232
52,026
35,533
0
2,014,611
7,609
0
0
Emissions
Rank
2
6
9
7
3
4
5
9
1
8
9
9
Total Industrial Emissions
within a 10-Mile Radius of
the Monitoring Location0
I
Pounds in
1997
3,471,078
37,511
0
25,073
443,296
147,020
511,797
2,296,884
3,463,330
345,472
940
0
Emissions
Rank
1
8
11
9
5
7
4
3
2
6
10
11
Total Number of Cars
Owned within a 10-Mile
Radius of the Monitoring
Location*1
Total Cars
256,716
22,611
5,616
86,381
1,503,540
360,257
45,196
70,410
60,821
124,765
22,848
23,650
Rank of
Total Cars
3
11
12
5
1
2
8
6
7
4
10
9
a This value was calculated as follows: (1) For each monitoring site, for each sampling event, the concentrations of the program-wide prevalent hydrocarbons
were summed. (2) For each monitoring site, the geometric mean of the sampling event totals was calculated.
'Industrial emissions were calculated from emissions data for TRI reporting year 1997 (TRI, 1997). The emissions reported in the table are the total air releases
of the hydrocarbons found to be program-wide prevalent in the 1998 UATMP. Acetylene was not reportable to TRI in 1997.
c Industrial emissions were calculated from emissions data for TRI reporting year 1997 (TRI, 1997).
d The total number of cars owned within a 10-mile radius was estimated based on a ratio of 0.74 cars per person (U.S. population of 260,000,000 and total cars in
U.S. of 193,400,000) Information from "Statistical Abstract of the United States", 1999, and the internet link at http://link-usa.com/zipcode/pop.htm
-------
Table 5-4
Comparison of Geometric Means of Program-Wide Prevalent Hydrocarbons with Total Air Releases Reported by Facilities
Within a 10-Mile Radius of UATMP Monitoring Stations
Benzene
Station Code
EPTX
BUVT
B2LA
HALA
RUVT
PARR
CANJ
BRVT
GREY
GALA
BUND
UNVT
ppbv
1.20
0.84
0.72
0.69
0.64
0.57
0.54
0.54
0.41
0.40
0.24
0.20
Ibs
14,120
0
103,342
105,655
0
0
30,956
0
0
632
0
0
Propylene
Station Code
EPTX
B2LA
HALA
BUVT
CANJ
RUVT
PARR
GALA
BRVT
GREY
BUND
UNVT
ppbv
1.48
1.45
1.45
1.19
0.95
0.90
0.84
0.78
0.78
0.44
0.32
0.25
Ibs
2,500
206,982
1,346,441
0
70,902
0
650
0
0
0
0
0
Toluene
Station Code
EPTX
BUVT
RUVT
B2LA
HALA
BRVT
CANJ
GALA
PARR
GREY
BUND
UNVT
ppbv
2.43
1.75
1.45
1.43
1.10
1.02
0.98
0.81
0.79
0.48
0.36
0.25
Ibs
31,506
12,768
0
171,389
277,466
13,836
78,187
34,811
4,590
0
0
0
to
to
-------
Table 5-4 (Continued)
Comparison of Geometric Means of Program-Wide Prevalent Hydrocarbons with Total Air Releases Reported by Facilities
Within a 10-Mile Radius of UATMP Monitoring Stations
Ethylbenzene
Station Code
EPTX
BUVT
B2LA
RUVT
PARR
BRVT
HALA
CANJ
GALA
GREY
BUND
UNVT
ppbv
0.46
0.30
0.30
0.25
0.20
0.18
0.17
0.16
0.15
0.10
0.08
0.07
Ibs
3,900
0
43,785
0
1,359
750
8,952
10,187
90
0
0
0
m-,/?-Xylene
Station Code
EPTX
BUVT
B2LA
RUVT
PARR
BRVT
CANJ
HALA
GALA
GREY
BUND
UNVT
ppbv
1.23
0.81
0.78
0.65
0.45
0.42
0.40
0.40
0.33
0.17
0.14
0.10
Ibs
0
0
0
0
510
0
0
276,097
0
0
0
0
oXylene
Station Code
EPTX
B2LA
BUVT
RUVT
PARR
BRVT
CANJ
HALA
GALA
GREY
BUND
UNVT
ppbv
0.59
0.43
0.40
0.33
0.24
0.22
0.21
0.20
0.17
0.09
0.08
0.06
Ibs
0
1,980
0
0
500
0
0
0
0
0
0
0
to
-------
6.0 Data Interpretation: Halogenated Hydrocarbons
Halogenated hydrocarbons are organic compounds that contain carbon, hydrogen, and
halogens—the chemical group that includes chlorine, bromine, and fluorine. Most halogenated
hydrocarbons are used for industrial purposes and as solvents, though some are produced
naturally (Godish, 1997). Once emitted to the air, many volatile halogenated hydrocarbons resist
photochemical breakdown and therefore persist in the atmosphere for relatively long periods of
time (Godish, 1997; Ramamoorthy and Ramamoorthy, 1997). These compounds can cause
chronic health effects as well as contribute to the formation of tropospheric ozone. Like
hydrocarbons, only the halogenated hydrocarbons with lower molecular weights are volatile, and
the sampling and analytical methods used in the 1998 UATMP measure a subset of 37 of these
volatile compounds.
The discussions in this chapter center on the general trends observed for the nine
program-wide prevalent halogenated hydrocarbons and consider halogenated hydrocarbon
concentrations quantified at the 12 monitoring locations, with respect to:
Correlations between concentrations of the program-wide prevalent halogenated
hydrocarbons and concentrations of other compounds measured at the same time at the
same monitoring location;
Correlations between concentrations of the program-wide prevalent halogenated
hydrocarbons and temperature;
Correlations between concentrations of the program-wide prevalent halogenated
hydrocarbons and meteorological parameters;
Temporal (annual) variations in halogenated hydrocarbon concentrations measured during
the 1994 through 1998 UATMPs;
Spatial variations in halogenated hydrocarbon concentrations measured during the 1998
UATMP; and
Relationship between spatial variations in halogenated hydrocarbon concentrations
measured during the 1998 UATMP and estimates of industrial emissions.
6-1
-------
6.1 Correlations Between Concentrations of Different Compounds
From the ambient air monitoring data collected for each sampling event at each site,
Pearson correlation coefficients were calculated to compare concentrations of the program-wide
prevalent compounds from the four groups of chemicals studied in the 1998 UATMP
(i.e., hydrocarbons, halogenated hydrocarbons, polar compounds, and carbonyls). The following
discussion summarizes the calculated correlations.
6.1.1 Correlations Between Halogenated Hydrocarbons and Hydrocarbons
Figure 6-1 shows the distribution of Pearson correlation coefficients calculated from the
ambient air monitoring data for the program-wide prevalent halogenated hydrocarbons and
program-wide prevalent hydrocarbons.
As the distribution of Pearson correlation coefficients in Figure 6-1 shows, ambient air
concentrations of the program-wide prevalent halogenated hydrocarbons measured during the
1998 UATMP were weakly correlated with ambient air concentrations of the program-wide
prevalent hydrocarbons. Approximately 25 percent of the correlation coefficients were between
+0.50 and +0.75, indicating a moderate positive correlation. Nearly 42 percent of the correlation
coefficients were between -0.25 and +0.25, indicating very weak or no correlation. However, the
average correlation is statistically significant (0.250 ± 0.174) across the 12 sites. These weak
correlations generally suggest that the factors that most strongly affect levels of halogenated
hydrocarbons in ambient air are different from the factors that affect ambient air concentrations of
hydrocarbons.
6-2
-------
6.1.2 Correlations Between Halogenated Hydrocarbons and Polar Compounds
Figure 6-1 shows the distribution of Pearson correlation coefficients calculated from the
ambient air monitoring data for the program-wide prevalent halogenated hydrocarbons and
program-wide prevalent polar compounds.
As the distribution of Pearson correlation coefficients in Figure 6-1 shows, ambient air
concentrations of the program-wide prevalent halogenated hydrocarbons measured during the
1998 UATMP were very weakly correlated with ambient air concentrations of the program-wide
prevalent polar compounds. Across all 12 sites, there was no statistical significance in the
correlations (0.146 ± 0.192). Less than 10 percent of the correlation coefficients were between
either +0.75 and+1, indicating few strong correlations. Nearly 58 percent of the correlation
coefficients were between -0.25 and +0.25, indicating very weak or no correlation. These weak
correlations generally suggest that the factors that most strongly affect levels of halogenated
hydrocarbons in ambient air are different from the factors that affect ambient air concentrations
of polar compounds.
6.1.3 Correlations Between Halogenated Hydrocarbons and Carbonyls
Figure 6-1 shows the distribution of Pearson correlation coefficients calculated from the
ambient air monitoring data for the program-wide prevalent halogenated hydrocarbons and
program-wide prevalent carbonyls.
The distribution of Pearson correlation coefficients in Figure 6-1 shows that ambient air
concentrations of the program-wide prevalent halogenated hydrocarbons measured during the
1998 UATMP were correlated with ambient air concentrations of the program-wide prevalent
carbonyls. Across all 12 sites, there was no statistical significance in the correlations (0.160 ±
0.175). Less than 10 percent of the correlation coefficients were between +0.50 and +0.75,
indicating a moderate positive correlation. Approximately 42 percent of the correlation
coefficients were between -0.25 and +0.25, indicating very weak or no correlation. These weak
correlations generally suggest that the factors that most strongly affect levels of halogenated
6-3
-------
hydrocarbons in ambient air are different from the factors that affect ambient air concentrations
of carbonyls.
6.2 Correlations Between Concentrations and Temperature
6.2.1 Temperature
According to Table 6-1, the program-wide prevalent halogenated hydrocarbons had
positive correlations with maximum, minimum, and average temperature across all twelve sites.
This observation would suggest that increasing temperature would relate to increasing measured
concentration of halogenated hydrocarbons. The highest positive correlations of halogenated
hydrocarbon concentration with maximum, minimum, and average temperature occurred at the
Hahnville, LA, site (0.570, 0.686, and 0.596, respectively). The Brattleboro, VT, site had the
strongest negative correlation of halogenated hydrocarbon concentration with minimum
temperature (-0.089).
Statistical significance of the correlation between the temperature parameters and the
measured halogenated hydrocarbon concentrations at the 95 percent confidence interval was also
calculated for each of the sites. As Table 6-1 shows, all of these correlations were statistically
significant.
6.2.2 Wind and Sea Level Pressure Information
According to Table 6-1, the program-wide prevalent halogenated hydrocarbons had a
negative correlation with the wind speed across the 12 sites. This observation would suggest that
high wind speeds tend to decrease the measured concentration of halogenated hydrocarbons. The
correlation between sea level pressure and the measured halogenated hydrocarbon concentration
was negative (-0.078 ± 0.100).
Statistical significance of the correlation between the wind speed and sea level pressure
and the measured halogenated hydrocarbon concentrations at the 95 percent confidence interval
6-4
-------
was also calculated for each of the sites. As Table 6-1 shows, only the correlation with the wind
speed was statistically significant. This observation suggests that increasing wind speeds reduce
the concentrations of the halogenated hydrocarbons, either by dilution or by removing the
compounds from the area where the measurements are being made.
6.2.3 Dew Point Temperature and Visibility
According to Table 6-1, the program-wide prevalent halogenated hydrocarbons generally
had positive correlations with both the dew point temperature and visibility. The highest positive
correlation of halogenated hydrocarbon concentration with dew point temperature and visibility
occurred at the Hahnville, LA, site (0.668) and the Baton Rouge (0.281) sites, respectively. The
strongest negative correlations for these two parameters occurred at the Texarkana, AR, site
(-0.003) and Camden, NJ (-0.223) sites, respectively.
Statistical significance of the correlation between the dew point temperature and visibility
and the measured halogenated hydrocarbon concentrations at the 95 percent confidence interval
was also calculated for each of the sites. As Table 6-1 shows, only the dew point temperature
exhibits a statistically significant positive correlation with measured halogenated hydrocarbon
concentration. This observation would suggest that halogenated hydrocarbons may increase with
increasing moisture.
6.3 Annual Variations
Table 6-2 presents average concentrations of program-wide prevalent halogenated
hydrocarbons at each of the 12 monitoring stations for the 1994 through 1998 UATMPs.
Overall, there is a general pattern of decreased concentrations of halogenated hydrocarbons from
1995 through 1998.
Readers should note that changes in concentrations can result from shifting prevailing
winds and might not necessarily indicate increases or decreases in emissions. In addition, readers
6-5
-------
should keep in mind that the concentrations of these compounds are quite low, generally less than
0.40 ppbv, and conclusions regarding annual variation should be made cautiously.
6.4 Spatial Variations
To provide a sense of how overall levels of halogenated hydrocarbons varied among the
UATMP monitoring locations, Figure 6-2, presents the geometric means of the sampling event
sums of the program-wide prevalent halogenated hydrocarbon concentrations for each monitoring
location. Unlike the concentration range seen for the hydrocarbons, little variation is
demonstrated for the concentrations and no strong trend is exhibited in geometric means data
presented in Figure 6-2. In addition, the geometric means for the halogenated compounds are
considerably lower (maximum of 3.2 ppbv) at all locations in comparison to the geometric means
for hydrocarbons and carbonyls.
i* * 4T-" _vsr *,<*** »" " ^ "** w 'iV^* •<• ^ T ' £*$£ ir-'ViV''""' "**"£"' ' ""*|
:It~is important to interpret Jke spatial variations^ described throughout this documentdn the \
^oper context,; These analyses compare and contrast ambient air qualify measured at
s^cific locations ^thin urban environments! Because'ambient air Quality can vary T
sstgjfficantljrwthm ur$ &
fambient air concentratiom throughout a city may differ sigwfacantfyfromithose measured at
k^ssp^dfic-VAT^mo^onngtShaions. ' , t 5 ^ , ^ «
6.5 The Impact of Motor Vehicle Emissions on Spatial Variations
Motor vehicles emit significantly greater quantities of hydrocarbons than they do
halogenated hydrocarbons. As a result, motor vehicle emissions generally do not correlate well
with airborne levels of halogenated hydrocarbons.
For purposes of comparison, both car ownership data and the observed levels of total
program-wide prevalent halogenated hydrocarbons are presented in Table 6-3, each ranked in
descending order. The data in this table show no relationship between car ownership as an
indicator of motor vehicle emissions and concentrations of halogenated hydrocarbons in ambient
air.
6-6
-------
6.6 The Impact of Industrial Emissions on Spatial Variations
For purposes of comparison, Table 6-3 summarizes emissions data for each monitoring
location and ranks each data set with the highest value assigned the rank of one. For each
monitoring location, Table 6-3 includes:
The geometric mean of the sum of the program-wide prevalent halogenated hydrocarbon
concentrations for each sampling event.
The sum of emissions of the 9 program-wide prevalent halogenated hydrocarbons
detected during the 1998 UATMP reported to TRI in 1997 by facilities within 10 miles of
the 1998 UATMP monitoring locations.
Total emissions reported to TRI in 1997 by facilities within 10 miles of the 1998 UATMP
monitoring locations.
As the table shows, the TRI emissions ranks for the 12 sites were fairly consistent with
the respective ranks of the total ambient air concentrations of the program-wide prevalent
halogenated hydrocarbons. Unique trends in the data presented in Table 6-3 include:
Two monitoring locations (i.e., Hahnville and Garyville, LA) had the highest
concentrations of halogenated hydrocarbons and among the highest emissions for total
industrial emissions reported to TRI. A distinct difference in the levels of industrial
emissions of program-wide prevalent hydrocarbons reported to TRI is seen between these
sites, despite the similarity in total TRI emissions. These two facilities are located
within 13 miles of each other. Many of the facilities with 10 miles of the Hahnville site
are within 15 miles of the Garyville site and may impact the air quality at the Garyville
monitoring station. The difference in the industrial emissions of program-wide prevalent
halogenated hydrocarbons reported to TRI is due to greater than 30,000 pounds of
chloromethane reported by the one facility that is within 10 miles of the Hahnville site,
but not within 10 miles of the Garyville site.
One monitoring location (i.e., Texarkana, AR) had among the lowest concentrations of
the program-wide prevalent hydrocarbons, but had relatively high levels of total industrial
emissions reported to TRI, and moderate emissions of program-wide prevalent
hydrocarbons.
6-7
-------
To examine the TRI emissions data more closely, Table 6-4 compares the reported air
releases for the individual program wide prevalent hydrocarbons (excluding acetylene) to the
corresponding geometric mean concentrations measured during the 1998 UATMP. For ease of
interpretation, Table 6-4 lists the monitoring locations in order of decreasing geometric mean
concentration for each compound. In general, the data in Table 6-4 indicate that industrial
emissions are not a dominating factor influencing levels of halogenated hydrocarbons in ambient
air. Readers should keep in mind that the concentrations of these compounds are quite low in
most cases, generally less than 1 ppbv, and conclusions regarding spatial variation should be
made cautiously.
Only two compounds, chloromethane and trichlorotrifluoroethane, appear to exhibit a
positive relationship between concentrations of pollutant detected at the monitoring site and
industrial emissions. In each case, the site with the highest reported concentration is also the site
with the highest reported industrial emissions. However, it should be noted that:
While the Baton Rouge, LA, site has the highest ambient concentration of
trichlorotrifluoroethane and is the only monitoring site for which the pollutant was
reported as an industrial emission, the levels of trichlorotrifluoroethane at Baton Rouge
(geometric mean of 0.16 ppbv) are not significantly different from the emissions at
Hahnville, LA (geometric mean of 0.13 ppbv).
Hahnville and Baton Rouge, LA, have the highest geometric mean concentrations of
chloromethane and are the only monitoring sites for which the pollutant was reported as
an industrial emission. However, the levels of chloromethane at Baton Rouge and
Hahnville are not significantly different from the emissions at the rest of the monitoring
sites. In addition, Hahnville has the highest geometric mean concentrations of
chloromethane (1.45 ppbv), but reported emissions of chloromethane are less than half
the emissions reported for Baton Rouge (geometric mean concentration of chloromethane
of 0.85 ppbv).
6-8
-------
Figure 6-1
Summary of Data Correlations Between Groups of Compounds
35
30
25
2 20
O
§ 15
S.
10
5
0
Correlations Between HdogenatedHyd-occrbons cndHydrocabons
.>.
* \
\
^
.
~~
N
,
-
x*1
,*t^,'
f'.''»
||
-lto-0.75 -0.75to-0.50-0.50to-0.25 -0.25toO OtoO.25 0.25to0.50 0.50to0.75 0.75tol
R cnge of P eas on Correlation Coefficients
Correlations Bet\AeenHdogenared Hydrocarbons and Polar Compounds
i 30
o 25
o 20
I
n
1
,
*•
:.
;"
I „.;•!
Id
•lto-0.75 -0.75to-0.50 -0.50to-0.25 -0.25toO OtoO.25 0.25to0.50 0.50to0.75 0.75tol
R onge of P ecrson Correlation Coefficients
Correlations B etveen Ccrbonyls andHdog^natedHydrocabons
55
2 20
1 15 +
• -
, s
-lto-0.75 -0.75to-0.50-0.50to-0.25 -0.25toO OtoO.25 0.25to0.60 0.50to0.75 0.75tol
R onge of P ears on Correlation Coefficients
6-9
-------
Figure 6-2
Geometric Mean of the Sums of Daily Concentrations (ppbv) of the Prevalent
Halogenated Hydrocarbons
3.5 -,
B _ 3
co >
£ a
Geometric Mean of th<
Daily Concentration
0 -»
in -"• en K>
0
•' !'?'
*
* >, * '
X
v>>
»^
0. ^
S> ***
» \
* •-• * 4*- ~L
'it *
•X. > f"r
1 -*- "
"^ ' ^~y V»z
^ ,
i-vV" * •'s ^
V^* ^ "*• ^
;^
"-.'Xi'
^ *°
*• '* v °
-•- ^ *
j
t f^;
GALA HALA EPTX PARR
Monitoring Location
-------
Table 6-1
Summary of Pearson Correlations for Selected Meteorological Parameters and Measured Halogenated
Hydrocarbon Concentrations
Meteorological Parameter
Maximum Temperature*
Minimum Temperature*
Average Temperature*
Wind Speed*
Sea Level Pressure
Dew Point Temperature*
Visibility
Average Correlation
0.328 ±0.108
0.265 ±0.1 30
0.299 ±0.1 14
-0.179 + 0.046
-0.078 ±0.100
0.276 ±0.122
0.014 ±0.102
Site with Highest Positive
Correlation (Value)
Hahnville, LA
(0.570)
Hahnville, LA
(0.686)
Hahnville, LA
(0.596)
None
Texarkana, AR
(0.218)
Hahnville, LA
(0.668)
Baton Rouge, LA
(0.281)
Site with Lowest
Negative Correlation
(Value)
None
Brattleboro, VT
(-0.089)
None
Hahnville, LA
(-0.284)
Beulah, ND
(-0.296)
Texarkana, AR
(-0.003)
Camden, NJ
(-0.223)
* Statistically significant across the 12 sites.
-------
Table 6-2
Average Concentrations (ppbv) of Program-Wide Prevalent Halogenated Hydrocarbons
for the 1998 UATMP Compared to the Same Compounds for Previous Years
1994
1995
1996
1997
1998
B2LA
1,1,1 -Trichloroethane
Carbon Tetrachloride
Chloromethane
Dichlorodifluoromethane
Methylene Chloride
p-Dichlorobenzene
Tetrachloroethylene
Trichlorofluoromethane
Trichlorotrifluoroethane
0.31
0.08
0.84
-
0.23
0.04
0.08
-
-
0.15
0.09
0.57
-
0.13
0.04
0.06
-
-
0.13
0.09
0.61
-
0.15
0.06
0.07
-
-
0.10
0.10
1.08
0.63
0.20
0.04
0.06
0.40
0.19
BRVT
1,1,1 -Trichloroethane
Carbon Tetrachloride
Chloromethane
Dichlorodifluoromethane
Methylene Chloride
p-Dichlorobenzene
Tetrachloroethylene
Trichlorofluoromethane
Trichlorotrifluoroethane
0.20
0.10
0.58
-
0.20
0.03
0.03
-
-
0.10
0.08
0.54
-
0.77
0.04
0.05
-
-
0.10
0.08
0.49
-
0.41
0.06
0.07
-
-
0.06
0.09
0.64
0.67
0.11
0.04
0.05
0.35
0.14
BUND . • ' i
1,1,1 -Trichloroethane
Carbon Tetrachloride
Chloromethane
Dichlorodifluoromethane
Methylene Chloride
p-Dichlorobenzene
Tetrachloroethylene
Trichlorofluoromethane
Trichlorotrifluoroethane
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.07
0.08
0.62
0.67
0.54
0.04
0.06
0.40
0.11
• Indicates compound was not included in the UATMP for that year.
6-12
-------
Table 6-2 (Continued)
Average Concentrations (ppbv) of Program-Wide Prevalent Halogenated Hydrocarbons
for the 1998 UATMP Compared to the Same Compounds for Previous Years
1994
1995
1996
1997
1998
BUVT
1 , 1 , 1 -Trichloroethane
Carbon Tetrachloride
Chloromethane
Dichlorodifluoromethane
Methylene Chloride
p-Dichlorobenzene
Tetrachloroethylene
Trichlorofluoromethane - .
Trichlorotrifluoroethane
0.21
0.08
0.64
-
0.15
0.03
0.03
-
-
0.10
0.08
0.51
-
0.09
0.04
0.03
. . -
-
0.11
0.08
0.56
•
0.13
0.06
0.07
-
-
0.06
0.09
0.64
0.67
0.21
0.04
0.04
0.37 .-
0.09
CANJ
1,1,1 -Trichloroethane 0.44
Carbon Tetrachloride 0.07
Chloromethane 0.72
Dichlorodifluoromethane
Methylene Chloride 1.18
p-Dichlorobenzene 0.05
Tetrachloroethylene 0.09
Trichlorofluoromethane
Trichlorotrifluoroethane
0.25
0.09
0.76
-
0.44
0.08
0.07
-
-
0.14
0.08
0.59
-
0.15
0.06
0.10
-
-
0.14
0.09
0.71
-
0.28
0.07
0.08
-
-
0.07
0.09
0.77
0.66
0.16
0.05
0.07
0.33
0.09
EPTX
1 , 1 , 1 -Trichloroethane
Carbon Tetrachloride
Chloromethane
Dichlorodifluoromethane
Methylene Chloride
p-Dichlorobenzene
Tetrachloroethylene
Trichlorofluoromethane
Trichlorotrifluoroethane
0.26
0.08
0.71
-
0.30
0.09
0.06
-
-
0.10
0.08
0.70
-
0.11
0.07
0.06
-
-
0.11
0.09
0.67
-
0.78
0.06
0.07
-
-
0.06
0.08
0.81
0.69
0.83
0.05
0.05
0.34
0.09
• Indicates compound was not included in the UATMP for that year.
6-13
-------
Table 6-2 (Continued)
Average Concentrations (ppbv) of Program-Wide Prevalent Halogenated Hydrocarbons
for the 1998 UATMP Compared to the Same Compounds for Previous Years
1994
1995
1996
1997
1998
GALA
1 , 1 , 1 -Trichloroethane
Carbon Tetrachloride
Chloromethane
Dichlorodifluoromethane
Methylene Chloride
p-Dichlorobenzene
Tetrachloroethylene
Trichlorofluoromethane
Trichlorotrifluoroethane
0.22
0.10
1.03
-
0.12
0.03
0.02
-
-
0.13
0.08
0.65
-
0.06
0.05
0.07
-
-
6.94
0.09
1.07
-
0.48
0.05
0.07
-
-
1.21
0.09
1.10
0.71
0.33
0.04
0.29
- 0.37
0.11
GREY
1,1,1 -Trichloroethane
Carbon Tetrachloride
Chloromethane
Dichlorodifluoromethane
Methylene Chloride
p-Dichlorobenzene
Tetrachloroethylene
Trichlorofluoromethane
Trichlorotrifluoroethane
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.06
0.07
-
-
0.06
0.08
0.66
0.59
0.26
0.04
0.06
0.31
0.08
HALA 'i
1 , 1 , 1 -Trichloroethane
Carbon Tetrachloride
Chloromethane
Dichlorodifluoromethane
Methylene Chloride
p-Dichlorobenzene
Tetrachloroethylene
Trichlorofluoromethane
Trichlorotrifluoroethane
0.23
0.09
0.88
-
1.78
0.04
0.04
-
-
0.16
0.09
0.61
-
0.07
0.04
0.06
-
-
0.17
0.09
1.13
-
0.12
0.05
0.07
-
-
0.09
0.09
1.83
0.66
0.17
0.04
0.17
0.35
0.13
• Indicates compound was not included in the UATMP for that year.
6-14
-------
Table 6-2 (Continued)
Average Concentrations (ppbv) of Program-Wide Prevalent Halogenated Hydrocarbons
for the 1998 UATMP Compared to the Same Compounds for Previous Years
1994
1995
1996
1997
1998
PARR
1,1,1 -Trichloroethane
Carbon Tetrachloride
Chloromethane
Dichlorodifluoromethane
Methylene Chloride
p-Dichlorobenzene
Tetrachloroethylene
Trichlorofluoromethane
Trichlorotrifluoroethane
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
-
0.11
0.10
0.91
-
0.19
0.05
0.06
-
-
0.06
0.08
0.80
0.65
1.01
0.04
0.06
- 0.29
0.11
RUVT
1 , 1 , 1 -Trichloroethane
Carbon Tetrachloride
Chloromethane
Dichlorodifluoromethane
Methylene Chloride
p-Dichlorobenzene
Tetrachloroethylene
Trichlorofluoromethane
Trichlorotrifluoroethane
0.18
0.08
0.55
-
0.44
0.03
0.05
-
-
0.14
0.08
0.49
-
0.08
0.04
0.05
-
-
0.10
0.09
0.52
-
0.16
0.05
0.06
-
-
0.06
0.09
0.64
0.70
0.15
0.04
0.05
0.34
0.09
UNVT
1,1,1 -Trichloroethane
Carbon Tetrachloride
Chloromethane
Dichlorodifluoromethane
Methylene Chloride
p-Dichlorobenzene
Tetrachloroethylene
Trichlorofluoromethane
Trichlorotrifluoroethane
0.23
0.07
0.56
-
0.15
0.03
0.02
-
-
0.08
0.08
0.52
-
0.06
0.04
0.05
-
-
0.09
0.08
0.56
-
0.08
0.06
0.09
-
-
0.06
0.08
0.68
0.61
0.13
0.04
0.05
0.33
0.10
Indicates compound was not included in the UATMP for that year.
6-15
-------
Table 6-3
Ranking of Monitoring Stations by Levels of Total Program-Wide Prevalent Halogenated Hydrocarbons
ON
0\
Monitoring
Location
B2LA
BRVT
BUND
BUVT
CANJ
EPTX
GALA
GREY
HALA
PARR
RUVT
UNVT
Geometric Means of the
Total Program- Wide
Prevalent Halogenated
Hydrocarbon
Concentrations1
ppbv
1998
2.61
2.13
2.54
2.17
2.23
2.77
3.14
2.12
2.96
2.73
2.14
2.04
Cone.
Rank
5
10
6
8
7
3
1
11
2
4
9
12
Industrial Emissions of
Program-Wide Prevalent
Halogenated
Hydrocarbons within a
10-Mile Radius of the
Monitoring Location5
Pounds in
1997
346,586
5,391
0
0
18,831
0
0
0
35,057
13,000
0
0
Emissions
Rank
1
5
6
6
3
6
6
6
2
4
6
6
Total Industrial
Emissions within a
10-Mile Radius of the
Monitoring Location0
Pounds in
1997
3,471,078
37,511
0
25,073
443,296
147,020
511,797
2,296,884
3,463,330
345,472
940
0
Emissions
Rank
1
8
11
9
5
7
4
3
2
6
10
11
Total Number of Cars
Owned within a 10-Mile
Radius of the Monitoring
Locationd
Total Cars
256,716
22,611
5,616
86,381
1,503,540
360,257
45,196
70,410
60,821
124,765
22,848
23,650
Rank of
Total Cars
3
11
12
5
1
2
8
6
7
4
10
9
' This value was calculated as follows: (1) For each monitoring site, for each sampling event, the concentrations of the program-wide prevalent hydrocarbons
were summed. (2) For each monitoring site, the geometric mean of the sampling event totals was calculated.
b Industrial emissions were calculated from emissions data for TRI reporting year 1997 (TRI, 1997). The emissions reported are the total air releases of the
halogenated hydrocarbons identified as program-wide prevalent for the 1998 UATMP.
c Industrial emissions were calculated from emissions data for TRI reporting year 1997 (TRI, 1997).
d The total number of cars owned within a 10-mile radius was estimated based on a ratio of 0.74 cars per person (U.S. population of 260,000,000 and total cars in
U.S. of 193,400,000). Information from "Statistical Abstract of the United States", 1999, and the internet link at http://link-usa.com/zipcode/pop.htm
-------
Table 6-4
Comparison of Geometric Means of Program-Wide Prevalent Halogenated Hydrocarbons with Total Air Releases Reported
by Facilities Within a 10-Mile Radius of UATMP Monitoring Stations
1,1,1 -Trichloroethane
Station Code
GALA
B2LA
HALA
CANJ
BUND
RUVT
BUVT
BRVT
PARR
UNVT
EPTX
GREY
ppbv
0.18
0.09
0.08
0.07
0.07
0.06
0.06
0.06
0.06
0.06
0.06
0.05
Ibs
0
4,505
0
18,630
0
0
0
0
0
0
0
0
p-Dichlorobenzene
Station Code
CANJ
PARR
EPTX
BRVT
HALA
UNVT
GREY
BUND
BUVT
B2LA
RUVT
GALA
ppbv
0.05
0.04
0.04
0.04
0.04
0.04
0.04
0.04
0.04
0.04
0.04
0.04
Ibs
0
0
0
0
0
0
0
0
0
0
0
0
Carbon Tetrachloride
Station Code
B2LA
HALA
RUVT
BUVT
BUND
BRVT
GALA
UNVT
CANJ
PARR
GREY
EPTX
oobv
0.09
0.09
0.09
0.09
0.08
0.08
0.08
0.08
0.08
0.08
0.08
0.07
Ibs
5,083
0
0
0
0
0
0
0
0
0
0
0
Dichlorodifluoromethane
Station Code
RUVT
BUVT
BRVT
HALA
BUND
EPTX
PARR
CANJ
B2LA
GALA
UNVT
GREY
ppbv
0.69
0.66
0.65
0.65
0.65
0.64
0.64
0.64
0.62
0.60
0.60
0.59
Ibs
0
0
0
0
0
0
0
0
14,595
0
0
0
Chloromethane
Station Code
HALA
B2LA
GALA
PARR
EPTX
CANJ
UNVT
GREY
BRVT
BUVT
BUND
RUVT
ppbv
1.45
0.85
0.83
0.77
0.76
0.73
0.67
0.66
0.64
0.63
0.62
0.63
Ibs
35,057
87,296
0
0
0
0
0
0
0
0
0
0
Methylene Chloride
Station Code
EPTX
BUND
PARR
GREY
B2LA
CANJ
BUVT
GALA
RUVT
HALA
BRVT
UNVT
ppbv
0.70
0.44
0.31
0.23
0.15
0.14
0.13
0.12
0.11
0.11
0.08
0.08
Ibs
0
0
13,000
0
9,176
201
0
0
0
0
5,391
0
-------
Table 6-4 (Continued)
Comparison of Geometric Means of Program-Wide Prevalent Halogenated Hydrocarbons with Total Air Releases Reported
by Facilities Within a 10-Mile Radius of UATMP Monitoring Stations
Tetrachloroethylene
Station Code
GALA
HALA
CANJ
GREY
BUND
PARR
B2LA
BRVT
UNVT
RUVT
BUVT
EPTX
ppbv
0.11
0.08
0.06
0.05
0.05
0.05
0.05
0.05
0.05
0.04
0.04
004
Ibs
0
0
0
0
0
0
3,361
0
0
0
0
0
Trichlorofluoromethane
Station Code
BUND
BUVT
B2LA
BRVT
RUVT
CANJ
GREY
UNVT
GALA
EPTX
HALA
PARR
oobv
0.38
0.36
0.34
0.34
0.34
0.32
0.31
0.30
0.30
0.30
0.29
0.25
Ibs
0
0
37,070
0
0
0
0
0
0
0
0
0
Trichlorotrifluoroethane
Station Code
B2LA
HALA
BRVT
PARR
BUND
GALA
UNVT
RUVT
CANJ
EPTX
BUVT
GREY
ppbv
0.16
0.13
0.12
0.10
0.10
0.10
0.09
0.09
0.09
0.09
0.08
0.08
Ibs
185,500
0
0
0
0
0
0
0
0
0
0
0
OS
I
oo
-------
7.0 Data Interpretation: Polar Compounds
Polar compounds (i.e., oxygenated compounds such as methyl tert-butyl ether, methyl
ethyl ketone, etc.) were added to the UATMP analyte list that included the volatile halogenated
hydrocarbons and selected hydrocarbons because of the nation-wide use of these types of
compounds as gasoline additives and the toxicity of these gasoline additives. Because of the
prevalence of compounds characteristic of motor vehicle emissions, any compounds used as
gasoline additives would be expected to be correspondingly prevalent. Other polar compounds
such as acetonitrile were added to the analyte list because the compounds were observed at high
concentrations at one or more monitoring sites.
The discussions in this chapter center on the general trends observed for the three
program-wide prevalent polar compounds and consider polar compound concentrations
quantified at the 12 monitoring locations, with respect to:
Correlations between concentrations of the program-wide prevalent polar compounds and
concentrations of other compounds measured at the same time at the same monitoring
location;
• Correlations between concentrations of the program-wide prevalent polar compounds and
temperature;
• Correlations between concentrations of the program-wide prevalent polar compounds and
meteorological parameters.
• Temporal (annual) variations in polar compound concentrations measured during the
1994 through 1998 UATMPs;
• Spatial variations in polar compound concentrations measured during the 1998 UATMP;
and
• Relationship between spatial variations in polar compound concentrations measured
during the 1998 UATMP and estimates based on the estimation of industrial emissions.
7-1
-------
7.1 Correlations Between Concentrations of Different Compounds
From the ambient air monitoring data collected for each sampling event at each site,
Pearson correlation coefficients were calculated to compare concentrations of the program-wide
prevalent compounds from the four groups of chemicals studied in the 1998 UATMP
(i.e., hydrocarbons, halogenated hydrocarbons, polar compounds, and carbonyls). The following
discussion summarizes the calculated correlations.
7.1.1 Correlations Between Hydrocarbons and Polar Compounds
Figure 7-1 shows the distribution of Pearson correlation coefficients calculated from the
ambient air monitoring data for the program-wide prevalent hydrocarbons and program-wide
prevalent polar compounds.
As the distribution of Pearson correlation coefficients in Figure 7-1 shows, ambient air
concentrations of the program-wide prevalent hydrocarbons measured during the 1998 UATMP
were very weakly correlated with ambient air concentrations of the program-wide prevalent polar
compounds. Approximately 16 percent of the correlation coefficients were between +0.50 and
+0.75, indicating a moderate positive correlation. Nearly 58 percent of the correlation
coefficients were between -0.25 and +0.25, indicating very weak or no correlation. However, the
average correlation was statistically significant across the 12 sites (0.199 ± 0.152). These weak
correlations generally suggest that the factors that most strongly affect levels of hydrocarbons in
ambient air are different from the factors that affect ambient air concentrations of polar
compounds.
7.1.2 Correlations Between Halogenated Hydrocarbons and Polar Compounds
Figure 7-1 shows the distribution of Pearson correlation coefficients calculated from the
ambient air monitoring data for the program-wide prevalent halogenated hydrocarbons and
program-wide prevalent polar compounds.
7-2
-------
As the distribution of Pearson correlation coefficients in Figure 7-1 shows, ambient air
concentrations of the program-wide prevalent halogenated hydrocarbons measured during the
1998 UATMP were very weakly correlated with ambient air concentrations of the program-wide
prevalent polar compounds. Across all 12 sites, there was no statistical significance in the
correlations (0.146 ± 0.192). Less than 10 percent of the correlation coefficients were between
either +0.75 and +1, indicating few strong correlations. Nearly 58 percent of the correlation
coefficients were between -0.25 and +0.25, indicating very weak or no correlation. These weak
correlations generally suggest that the factors that most strongly affect levels of halogenated
hydrocarbons in ambient air are different from the factors that affect ambient air concentrations
of polar compounds.
7.1.3 Correlations Between Carbonyls and Polar Compounds
Figure 7-1 shows the distribution of Pearson correlation coefficients calculated from the
ambient air monitoring data for pairs of the program-wide prevalent polar compounds and
program-wide prevalent carbonyls.
The distribution of Pearson correlation coefficients in Figure 7-1 indicates a weak
correlation between ambient air concentrations of the program-wide prevalent carbonyls
measured during the 1998 UATMP and those of program-wide prevalent polar compounds.
Approximately 25 percent of the correlation coefficients were between -0.25 and -0.50,
indicating a moderate negative correlation. Approximately 58 percent of the correlation
coefficients were between -0.25 and +0.25, indicating very weak or no correlation.
7.2 Correlations Between Concentrations and Temperature
7.2.1 Temperature
According to Table 7-1, the program-wide prevalent polar compounds had a positive
correlation for maximum temperature and negative correlations for minimum and average
temperature across all 12 sites. The highest positive correlations of polar compound
7-3
-------
concentrations with maximum and average temperature occurred at the Little Rock, AR, site
(0.401 and 0.366, respectively), while the Burlington, VT, site had the highest positive
correlation for minimum temperature (0.321). The Baton Rouge, LA, site had the strongest
negative correlation of polar compound concentration with all three temperature parameters
(-0.478, -0.326, and -0.406, respectively).
Statistical significance of the correlation between the temperature parameters and the
measured polar compound concentrations at the 95 percent confidence interval was also
calculated for each of the sites. As Table 7-1 shows, none of these correlations were statistically
significant.
7.2.2 Wind and Sea Level Pressure Information
According to Table 7-1, the program-wide prevalent polar compounds had positive
correlations with the wind speed across the 12 sites. The highest positive correlation of polar
hydrocarbon concentration with the wind speed occurred at the Rutland, VT, site (-0.524) while
the Texarkana, AR, site had the strongest negative correlation with the wind speed (-0.516).
The correlation between sea level pressure and polar compound concentrations was
negative across the 12 sites. The Burlington, VT, site had the strongest negative correlation
(-0.462), while the Beulah, ND, site had the highest positive correlation (0.271).
Statistical significance of the correlation between the wind speed and sea level pressure
with the measured polar compound concentrations at the 95 percent confidence interval was also
calculated across the 12 sites. As Table 7-1 shows, neither of these correlations were statistically
significant.
7.2.3 Dew Point Temperature and Visibility
According to Table 7-1, the program-wide prevalent polar compounds had a positive
correlation with the dew point temperature. The highest positive correlation of polar compound
7-4
-------
concentrations with the dew point temperature occurred at the Camden, NJ, site (0.388), while
the strongest negative correlation for this parameter occurred at the Garryville, LA, site (-0.369).
Visibility showed a negative correlation with the polar compound concentrations across
the 12 sites. The strongest negative correlation occurred at the Texarkana, AR, site (-0.518),
while the highest positive correlation occurred at the Garyville, LA, site (0.134).
Statistical significance of the correlation between the dew point temperature and the
visibility with the measured polar compound concentrations at the 95 percent confidence interval
was also calculated across the 12 sites. As Table 7-1 shows, only the visibility correlation was
statistically significant, suggesting that as the visibility decreases (indicating increased haziness)
the polar compound concentrations increase.
7.3 Annual Variations
This section briefly describes the annual variation in ambient air concentrations of the
program-wide prevalent polar compounds. Readers should note that changes in concentrations
can result from shifting prevailing winds and might not necessarily indicate increases or
decreases in emissions. Table 7-2 presents average concentrations of program-wide prevalent
polar compounds at each of the 12 monitoring stations for the 1997 and 1998 UATMPs. These
data illustrate the following general trends:
With the exception of the Baton Rouge, LA, monitoring site, acetonitrile concentrations
are lower in 1998 than in 1997. It should be noted that the Baton Rouge, LA, acetonitrile
concentrations are orders of magnitude greater than at any other monitoring site.
With the exception of the Baton Rouge and Garyville, LA, monitoring sites, methyl ethyl
ketone concentrations are higher in 1998 than in 1997. Readers should keep in mind that
the concentrations of this compound are quite low, generally less than 1 ppbv, and
conclusions regarding annual variation should be made cautiously.
7-5
-------
7.4 Spatial Variations
To provide a sense of how overall levels of polar compounds varied among the UATMP
monitoring locations, Figure 7-2 presents the geometric means of the sampling event sums for
the program-wide prevalent polar compound concentrations at each monitoring location. With
the exception of the large peak seen for the Baton Rouge, LA, site, little variation is
demonstrated for the concentrations and no strong trend is exhibited in geometric means data
presented in Figure 7-2. Aside from the Baton Rouge, LA, site, the geometric means for the
polar compounds are considerably lower (maximum of 1.9 ppbv) at all locations in comparison
to the geometric means for hydrocarbons and carbonyls.
The large peak seen for the Baton Rouge, LA, site is the result of very high
concentrations of acetonitrile in some of the samples. Considerable variation is seen in the levels
of acetonitrile at this monitoring site, with values ranging from 110 ppbv to concentrations below
the method detection limit.
7.5 The Impact of Motor Vehicle Emissions on Spatial Variations
For purposes of comparison, both car ownership data and the observed levels of total
program-wide prevalent polar compounds are presented in Table 7-3, each ranked in descending
order. The data in this table indicate a possible correlation between car ownership as an indicator
of motor vehicle emissions and concentrations of polar compounds in ambient air, but exceptions
are also seen:
Concentrations of program-wide prevalent polar compounds were lowest at the Beulah,
ND, monitoring site. This is also the site with the lowest total number of cars.
Concentrations of program-wide prevalent polar compounds were highest at the Baton
Rouge, LA, monitoring site. This site has the third highest total number of cars.
Conversely, the Texarkana, AR, site has the second highest concentrations of program-
wide prevalent polar compounds, but ranks in middle level for number of cars.
7-6
-------
7.6 The Impact of Industrial Emissions on Spatial Variations
For purposes of comparison, Table 7-3 summarizes emissions data for each monitoring
location, and ranks each data set with the highest value assigned the rank of one. For each
monitoring location, Table 7-3 includes:
The geometric mean of the sum of the program-wide prevalent polar compound
concentrations for each sampling event.
The sum of emissions for 8 of the 9 program-wide prevalent polar compounds detected
during the 1998 UATMP, as reported to TRI in 1997 by facilities within 10 miles of the
1998 UATMP monitoring locations. The table does not account for emissions of
bromoform because industries are not required to disclose releases of this compound to
TRI.
Total emissions reported to TRI in 1997 by facilities within 10 miles of the 1998 UATMP
monitoring locations.
As the table shows, the TRI emissions ranks for the 12 sites were very consistent with the
respective rank of the total ambient air concentration of the program-wide prevalent polar
compounds. It should be noted that 6 of the 12 monitoring sites did not report any industrial
emissions of program-wide prevalent polar compounds. The relationship between ambient air
concentrations and industrial emissions is illustrated by the following:
The Baton Rouge, LA, monitoring site reported the highest concentrations of program-
wide prevalent polar compounds as well as the highest industrial emissions of both
program-wide prevalent and total polar compounds.
The Beulah, ND, and Underhill, VT, monitoring sites reported the lowest concentrations
of program-wide prevalent polar compounds as well as the lowest industrial emissions of
total polar compounds and no industrial emissions of program-wide prevalent polar
compounds.
To examine the TRI emissions data more closely, Table 7-4 compares the reported air releases
for acetonitrile, methyl ethyl ketone (MEK), and methyl tert-buty] ether (MTBE) to the
corresponding geometric mean concentrations measured during the 1998 UATMP. For ease of
7-7
-------
interpretation, Table 7-4 lists the monitoring locations in order of decreasing geometric mean
concentration for each compound. At first glance, it appears that there may be a relationship
between industrial emissions and ambient air concentrations, but it must be noted that:
While the acetonitrile emissions at Baton Rouge are significantly higher than at any other
site, higher levels of industrial emissions of acetonitrile are reported for the
Hahnville, LA, monitoring location.
While industrial emissions of MEK are reported for the monitoring sites with the two
highest levels of MEK ambient air concentrations, significant levels of MEK are reported
by industrial facilities near three other monitoring locations.
Facilities within 10 miles of Baton Rouge, LA, report high levels of industrial emissions
of MTBE, but concentrations of MTBE measured at Baton Rouge are near or below the
detection limit.
7-8
-------
Figure 7-1
Summary of Data Correlations Between Groups of Compounds
35
Percent of Sites
- — • NJ ro C
3 Ul O C71 C
Correlations BetvieenHyttooorbons ondPolcrCompouncfe
\{°**
s
||
»S;i
.^v ^
p—
P
||
-Ho-0.75 -0.75to-0.50 -0.50to-0.25 -0.25toO OtoO.25 0.25to0.50 0.50to0.75 0.75tol
R cnge of P ears on Correlation Coeff icicents
Corrections BervueenHdogexfedHydrooabons cndPola ConpoLnds
o
c
a.
::,gl
li
,
— — .
}
•
'
N
I
'i-
' 4
*" ' \
i*
^
pi
III)
-lto-0.75 -0.75to-0.50 -0.50to-0.25 -0.25toO OtoO.25 0.25to0.50 0.50to0.75 0.75tol
Rongeof Reason Correction Coefficients
Percent of Sites
Correlations Between Cabonyis ondPolaCompounct
>?s
/
' '
,
:•'••'*
:3
M.-
.1 10-0.75 -0.75to-0.50 -0.50lo-0.25 -0.2StoO OtoO.25 0.25to0.50 O.MtoO.75 0.75tol
R ono^ of P eas on Correlation Coefficients
7-9
-------
Figure 7-2
Geometric Mean of the Sums of Daily Concentrations (ppbv) of the Prevalent Polar
Compounds
-4
i
O
16
0_ 14
W .Q
I 8-12
CO
w
£ o
o 75
c -s
ra S
S °
0 O
•=o
0) >.
II
C5
10
B2LA
GFEY CANJ BPTX
HALA BRVT RUVT BUVT GAU\ PARR UNVT BUND
Monitoring Location
-------
Table 7-1
Summary of Pearson Correlations for Selected Meteorological Parameters and Measured Polar Hydrocarbon Concentrations
Meteorological Parameter
Maximum Temperature
Minimum Temperature
Average Temperature
Wind Speed
Sea Level Pressure
Dew Point Temperature
Visibility*
Average Correlation
-0.002 ±0.1 57
0.020 ±0.1 64
0.007 ±0.161
0.030 ±0.1 68
-0.058 ±0.109
0.018 + 0.158
-0.165 + 0.137
Site with Highest
Positive Correlation
(Value)
Little Rock, AR
(0.401)
Burlington, VT
(0.321)
Little Rock, AR
(0.366)
Rutland, VT
(0.524)
Beulah, ND
(0.271)
Camden, NJ
(0.388)
Garyville, LA
(0.134)
Site with Strongest
Negative Correlation
(Value)
Baton Rouge, LA
(-0.478)
Baton Rouge, LA
(-0.326)
Baton Rouge, LA
(-0.406)
Texarkana, AR
(-0.516)
Burlington, VT
(-0.463)
Garyville, LA
(-0.369)
Texarkana, AR
(-0.518)
* Statistically significant across all 12 sites.
-------
Table 7-2
Average Concentrations (ppbv) of Program-Wide Prevalent Polar Compounds for the
1998 UATMP Compared to the Same Compounds for Previous Years
1994 1995 1996 1997
1998
B2LA
Acetonitrile
Methyl Ethyl Ketone
Methyl tert-Butyl Ether
139.50
1.13
0.13
39.60
1.07
0.07
BRVT
Acetonitrile
Methyl Ethyl Ketone
Methyl tert-Butyl Ether
0.24
0.46
0.30
1.04
0.94
0.36
BUND
Acetonitrile
Methyl Ethyl Ketone
Methyl terr-Butyl Ether
.
0.04
*
0.02
BUVT
Acetonitrile
Methyl Ethyl Ketone
Methyl tert-Butyl Ether
0.31
0.41
0.31
0.89
0.66
0.36
CANJ
Acetonitrile
Methyl Ethyl Ketone
Methyl terf-Butyl Ether
0.31
0.63
1.19
0.35
0.73
0.92
EPTX
Acetonitrile
Methyl Ethyl Ketone
Methyl terf-Butyl Ether
0.24
0.65
0.09
2.36
0.98
0.39
GALA
Acetonitrile
Methyl Ethyl Ketone
Methyl tert-Butyl Ether
1.33
1.79
0.03
1.72
0.69
0.04
GREY
Acetonitrile
Methyl Ethyl Ketone
Methyl tert-Buiyl Ether
0.02
2.51
1.18
0.02
HALA
Acetonitrile
Methyl Ethyl Ketone
Methyl terf-Butvl Ether
0.66
0.74
0.04
5.86
0.79
0.19
- Indicates compound was not included in the UATMP for that year.
*Analytical results are considered invalid.
7-12
-------
Table 7-2 (Continued)
Average Concentrations (ppbv) of Program-Wide Prevalent Polar Compounds for the
1998 UATMP Compared to the Same Compounds for Previous Years
1994 1995 1996 1997
1998
PARR «
Acetonitrile
Methyl Ethyl Ketone
Methyl tert-Bulyl Ether
0.25
0.71
0.03
0.26
0.73
0.02
RUVT
Acetonitrile
Methyl Ethyl Ketone
Methyl tert-Buty\ Ether
0.65
0.51
0.23
1.24
0.62
0.28
UNVT
Acetonitrile "
Methyl Ethyl Ketone
Methyl tert-Butyl Ether
0.31
0.35
0.05
0.44
0.43
0.02
- Indicates compound was not included in the UATMP for that year.
*Analytical results are considered invalid.
7-13
-------
Table 7-3
Ranking of Monitoring Stations by Levels of Total Program-Wide Prevalent Polar Compounds
Monitoring
Location
B2LA
BRVT
BUND
BUVT
CANJ
EPTX
GALA
GREY
HALA
PARR
RUVT
UNVT
Geometric Means of the
Total Program-Wide
Prevalent Polar Compound
Concentrations0
ppbv
1998
14.82
1.58
0.55
1.19
1.78
1.76
1.11
1.98
1.60
0.90
1.43
0.62
Cone.
Rank
1
6
12
8
3
4
9
2
5
10
7
11
Industrial Emissions of
Program-Wide Prevalent
Polar Compounds within a
10-Mile Radius of the
Monitoring Location15
Pounds in
1997
350,568
0
0
0
1 10,625
2,560
0
15,230
143,640
15,458
0
0
Emissions
Rank
1
7
7
7
3
6
3
5
2
4
7
7
Total Industrial
Emissions within a
10-Mile Radius of the
Monitoring Location0
Pounds in
1997
3,471,078
37,511
0
25,073
443,296
147,020
511,797
2,296,884
3,463,330
345,472
940
0
Emissions
Rank
1
8
11
9
5
7
4
3
2
6
10
11
Total Number of Cars
Owned within a 10-Mile
Radius of the Monitoring
Location6
Total Cars
256,716
22,611
5,616
86,381
1,503,540
360,257
45,196
70,410
60,821
124,765
22,848
23,650
Rank of
Total Cars
3
11
12
5
1
2
8
6
7
4
10
9
a This value was calculated as follows: (1) For each monitoring site, for each sampling event, the concentrations of the program-wide prevalent hydrocarbons
were summed. (2) For each monitoring site, the geometric mean of the sampling event totals was calculated.
""Industrial emissions were calculated from emissions data for TRI reporting year 1997 (TRI, 1997). The emissions reported are the total air releases of the polar
compounds identified as program-wide prevalent for the 1998 UATMP.
c Industrial emissions were calculated from emissions data for TRI reporting year 1997 (TRI, 1997).
d The total number of cars owned within a 10-mile radius was estimated based on a ratio of 0.74 cars per person (U.S. population of 260,000,000 and total cars in
U j^f 193,400,000). Information from "Statistical Abstract of the United States", 1999, and the internet link at http://link-usa.com/zipcode/pop.htm
-------
Table 7-4
Comparison of Geometric Means of Program-Wide Prevalent Polar Compounds with Total
Air Releases Reported by Facilities Within a 10-Mile Radius of UATMP Monitoring
Stations
Acetonitrile
Station
Code
B2LA
BUND
GREY
HALA
RUVT
GALA
BRVT
EPTX
BUVT
CANJ
UNVT
PARR
ppbv
6.78
0.58
0.45
0.33
0.33
0.23
0.20
0.20
0.17
0.16
0.16
0.15
Ibs
7,000
0
0
15,140
0
0
0
0
0
0
0
0
Methyl Ethyl Ketone
Station
Code
B2LA
GREY
EPTX
BRVT
HALA
PARR
CANJ
RUVT
GALA
BUVT
UNVT
BUND
pobv
1.01
0.97
0.84
0.66
0.65
0.63
0.61
0.56
0.56
0.49
0.36
fa)
Ibs
186,282
15,230
0
0
101,000
15,458
6,945
0
0
0
0
NA
Methyl terr-Butyl Ether
Station
Code
CANJ
BUVT
BRVT
RUVT
EPTX
HALA
B2LA
GALA
BUND
GREY
PARR
UNVT
ppbv
0.78
0.30
0.29
0.22
0.15
0.05
0.03
0.02
0.02
0.02
0.02
0.02
Ibs
103,680
0
0
0
2,560
27,500
'157,286
0
0
0
0
0
(a) MEK is not reported for the Beulah, ND, site due to sample contamination.
7-15
-------
8.0 Data Interpretation: Carbonyls
Carbonyls are organic compounds characterized by their composition of carbon,
hydrogen, and oxygen, and by the presence of at least one carbon-oxygen double bond. Several
different factors are known to affect ambient air concentrations of carbonyls, but most notably:
Combustion sources, motor vehicles, and various industrial processes that emit carbonyls
directly to the atmosphere;
Photochemical reactions that form carbonyls in the air, typically from airborne
hydrocarbons; and
Photochemical reactions that consume carbonyls in the air, generally by photolysis or by
reaction with hydroxyl radicals (Seinfeld, 1986). .
As noted in Section 2, the 1998 UATMP sampling and analytical methods measured
concentrations of 16 carbonyl compounds. The discussions in this chapter center on the general
trends observed for four program-wide prevalent carbonyls and consider carbonyl concentrations
quantified at the 12 monitoring locations, with respect to:
Correlations between concentrations of the program-wide prevalent carbonyls and
concentrations of other compounds measured at the same time at the same monitoring
location;
Correlations between concentrations of the program-wide prevalent carbonyls and
temperature;
Correlations between concentrations of the program-wide prevalent carbonyls and
meteorological parameters;
Temporal (annual) variations in carbonyl concentrations measured during the 1994
through 1998 UATMPs;
Spatial variations in carbonyl concentrations measured during the 1998 UATMP;
Relationship between spatial variations in carbonyl concentrations measured during the
1998 UATMP and estimates based on estimation of motor vehicle emissions; and
8-1
-------
Relationship between spatial variations in carbonyl concentrations measured during the
1998 UATMP and estimates based on estimation of industrial emissions.
•> - ** V ~" / " ' f v •»< ' «, \ \ "^^ .vi"1^ ^T-j'-f1 ^ A
TTiii? report presents only.pairwise correlations (i.e.^correlations
-------
compounds, or that the program-wide prevalent hydrocarbon and carbonyl species originate from
different sources.
8.1.2 Correlations Between Carbonyls and Halogenated Hydrocarbons
Figure 8-1 shows the distribution of Pearson correlation coefficients calculated from the
ambient air monitoring data for the program-wide prevalent carbonyls and program-wide
prevalent halogenated hydrocarbons.
The distribution of Pearson correlation coefficients in Figure 8-1 shows that ambient air
concentrations of the program-wide prevalent halogenated hydrocarbons measured during the
1998 UATMP were correlated weakly with ambient air concentrations of the program-wide
prevalent carbonyls. Across all 12 sites, there was no statistical significance in the correlations
(0.160 ± 0.175). Less than 10 percent of the correlation coefficients were between +0.50 and
+0.75, indicating a moderate positive correlation. Approximately 42 percent of the correlation
coefficients were between -0.25 and +0.25, indicating very weak or no correlation. These weak
correlations generally suggest that the factors that most strongly affect levels of halogenated
hydrocarbons in ambient air are different from the factors that affect ambient air concentrations
of carbonyls.
8.1.3 Correlations Between Carbonyls and Polar Compounds
Figure 8-1 shows the distribution of Pearson correlation coefficients calculated from the
ambient air monitoring data for the program-wide prevalent carbonyls and program-wide
prevalent polar compounds.
The distribution of Pearson correlation coefficients in Figure 8-1 indicates a weak
correlation between ambient air concentrations of the program-wide prevalent carbonyls
measured during the 1998 UATMP and those of program-wide prevalent polar compounds.
Approximately 25 percent of the correlation coefficients were between -0.25 and -0.50,
indicating a moderate negative correlation. Approximately 58 percent of the correlation
8-3
-------
coefficients were between -0.25 and +0.25, indicating very weak or no correlation. These weak
correlations generally suggest that the factors that most strongly affect levels of polar compounds
in ambient air are different from the factors that affect ambient air concentrations of carbonyls.
8.2 Correlations Between Concentrations and Meteorological Parameters
8.2.1 Temperature
According to Table 8-1, the program-wide prevalent carbonyls had positive correlations
with maximum, minimum, and average temperature across all twelve sites. This observation
would suggest that increasing temperature would relateto increasing measured concentration of
carbonyls. The highest positive correlations of carbonyl concentrations with these
meteorological parameters all occurred at the Beulah, ND, site (0.681, 0.618, and 0.698,
respectively). The Hahnville, LA, site had the strongest negative correlation of carbonyl
concentrations with the three temperature parameters (-0.417, -0.484, -0.419, respectively).
Statistical significance of the correlation between the temperature parameters and the
measured carbonyl concentrations at the 95 percent confidence interval was also calculated
across the 12 sites. As Table 8-1 shows, all of these correlations were statistically significant,
suggesting that air temperature is a key component in the measured carbonyl concentrations
tendency.
8.2.2 Wind and Sea Level Pressure Information
According to Table 8-1, the program-wide prevalent carbonyls had a negative correlation
with wind speed across the 12 sites. The Baton Rouge, LA, site had the strongest negative
correlation (0.494). This observation would suggest that slow-moving air tends to increase the
measured concentrations of carbonyls. The strongest negative correlation of carbonyl
concentration with the sea level pressure occurred at the Beulah, ND, site (-0.344) while the
Hahnville, LA, site had the highest positive correlation (0.568).
8-4
-------
Statistical significance of the correlation between the wind speed and sea level pressure
with the measured carbonyl concentrations at the 95 percent confidence interval was also
calculated for each of the sites. As Table 8-1 shows, only the correlation with wind speed was
statistically significant. This observation suggests that increasing wind speeds reduce the
concentrations of the carbonyls, either by dilution or by removing the compounds from the area
where the measurements are being made.
8.2.3 Dew Point Temperature and Visibility
According to Table 8-1, the program-wide prevalent carbonyls generally had positive
correlations with both the dew point temperature and visibility. The highest positive correlation
of carbonyl concentration with the dew point temperature and the visibility occurred at the
Beulah, ND, site (0.643) and the Texarkana, AR, (0.349) site. The Hahnville site had the
strongest negative correlations for both parameters (-0.457 and -0.551, respectively).
Statistical significance of the correlation between these parameters and the measured
carbonyl concentrations at the 95 percent confidence interval was also calculated for each of the
sites. As Table 8-1 shows, only the dew point temperature was statistically significant, which
suggests that carbonyl concentrations may increase with increasing moisture.
8.3 Annual Variations
This section briefly describes the annual variation in ambient air concentrations of the
program-wide prevalent carbonyls. Readers should note that changes in concentrations can result
from shifting prevailing winds and might not necessarily indicate increases or decreases in
emissions. Table 8-2 presents average concentrations of program-wide prevalent carbonyls at
each of the 12 monitoring stations for the 1994 through 1998 UATMPs. These data illustrate the
following general trends:
With only a few exceptions, the concentrations of acetaldehyde and formaldehyde have
decreased every year at every monitoring site.
8-5
-------
No annual variation trend is apparent for acetone concentrations.
With the exception of Camden, NJ, butyr/isobutyraldehyde concentrations have exhibited
a trend of decreasing concentrations from 1995 through 1998.
8.4 Spatial Variations
To provide a sense of how overall levels of polar compounds varied among the UATMP
monitoring locations, Figure 8-2 presents the geometric means of the sampling event sums for
the program-wide prevalent carbonyl concentrations at each monitoring location.
To examine the TRI emissions data more closely, Table 8-3 compares the reported air
releases for the individual program-wide prevalent carbonyls (excluding acetone) to the
corresponding geometric mean concentrations measured during the 1998 UATMP. For ease of
interpretation, Table 8-3 lists the monitoring locations in order of decreasing geometric mean
concentration for each compound. No clear relationship between industrial emissions and
ambient air concentrations of carbonyls is demonstrated by the data presented in Table 8-3.
8.5 The Impact of Motor Vehicle Emissions on Spatial Variations
Motor vehicles are thought to contribute to variations in carbonyl concentrations in
ambient air. This report uses two parameters to evaluate the impact of motor vehicle emissions
on ambient air quality:
• Car ownership data; and
• Motor vehicle emissions profiles.
8.5.1 Car Ownership Data
As an indicator of motor vehicle emissions near the UATMP monitoring locations,
Table 8-4 presents estimates of the number of cars owned by residents within 10 miles of each
monitoring location. For purposes of comparison, both car ownership data and the observed
levels of total program-wide prevalent carbonyls are presented in Table 8-4, ranked in
8-6
-------
descending order. The data in the table indicate some correlation between car ownership data
and ambient air concentrations of carbonyls:
The monitoring sites at El Paso, TX, and Camden, NJ, reported the highest concentrations
of program-wide prevalent carbonyls and also have the highest numbers of cars within
10 miles of the sites.
The Beulah, ND, and Underhill, VT, sites report low concentrations of program-wide
prevalent carbonyls and low numbers of cars within 10 miles of the sites. However, very
little correlation can be seen between reported concentrations and car ownership at the
remaining monitoring sites.
Readers should keep in mind other factors that might impact the reliability of car ownership data
as an indicator of ambient air monitoring data results:
Higher car ownership within a 10-mile radius does not necessarily imply increased motor
vehicle use in the immediate vicinity of a monitoring location. Conversely, sparsely
populated regions often contain heavily traveled roadways.
Emissions sources in the area other than motor vehicles may significantly affect levels of
carbonyls in the ambient air.
8.5.2 Motor Vehicles Emissions Profiles
While the roadside study cited in Section 5 did not consider concentrations of carbonyls,
analysis of concentration ratios for selected carbonyls indicates that motor vehicle emissions
influence ambient levels of these compounds. More specifically, if motor vehicles indeed
significantly affect ambient air concentrations of carbonyls, it would be expected that ratios of
concentrations of carbonyls to concentrations of any BTEX compound would be consistent
across monitoring locations. As a test of this hypothesis, Figure 8-3 shows ratios between the
concentrations of four carbonyls—acrolein, benzaldehyde, and butyr/isobutyraldehyde—and
concentrations of m-,p-xylene for the 1998 UATMP monitoring locations. With the exception of
El Paso, TX, the ratios shown in Figure 8-3 are somewhat similar for the 12 monitoring
8-7
-------
locations, which suggests that emissions from motor vehicles may affect airborne levels of these
three carbonyl compounds.
8.6 The Impact of Industrial Emissions on Spatial Variations
For purposes of comparison, Table 8-4 summarizes emissions data for each monitoring
location and ranks each data set with the highest value assigned the rank of one. For each
monitoring location, Table 8-4 includes:
The geometric mean of the sum of the program-wide prevalent carbonyl concentrations
for each sampling event.
The sum of emissions of 3 of the 4 program-wide prevalent carbonyls detected during the
1998 UATMP (acetaldehyde, butyr/isobutyraldehyde, and formaldehyde) as reported to
TRI in 1997 by facilities within 10 miles of the 1998 UATMP monitoring locations. The
table does not account for emissions of acetone because industries are not required to
disclose releases of these compounds to TRI.
Total emissions reported to TRI in 1997 by facilities within 10 miles of the 1998 UATMP
monitoring locations.
As the table shows, the TRI emissions ranks for the 12 sites were not consistent with the
respective rank of the total ambient air concentration of the program-wide prevalent carbonyls. It
should be noted that 8 of the 12 monitoring sites did not report any industrial emissions of
program-wide prevalent carbonyl compounds. To examine the TRI emissions data more closely,
Table 8-4 compares the reported air releases for the individual program-wide prevalent carbonyls
(excluding acetone) to the corresponding geometric mean concentrations measured during the
1998 UATMP. The weakness of the relationship between ambient air concentrations and
industrial emissions is illustrated by the following:
El Paso, TX, and Camden, NJ, reported the highest concentrations of the program-wide
prevalent carbonyls, but had moderate levels of total industrial emissions reported to TRI
and no industrial emissions of program-wide prevalent carbonyl compounds.
8-8
-------
Other monitoring locations (e.g., Hahnville and Baton Rouge, LA) had relatively low
concentrations of carbonyls, but relatively high levels of emissions reported to TRI.
8-9
-------
Figure 8-1
Summary of Data Correlations Between Groups of Compounds
Correlations B etvteen Ccrbonyls axlHyaroocrbons
Ml
.£
^ ?n-
o
£ ,5
I
,.
•
^ T
-lto-0.75 -0.75to-0.50-0.50to-0.25 -0.25toO OtoO.25 0.25100.50 0.50to0.75 0.75tol
R cnge of P eas on Correlation Coefficients
45-
40
35
«: M
iio
Percent o
n 0 oi O t
0
Correlations B etween Corbonyls cndHdogenatedHytfoccrbons
n
I- 1
- v
"^ •?
f*
*
"y
~> /
{* > /
n
••J
-lto-0.75 -0.75to-0.60 -0.50to-0.25 -0.25toO OtoO.25 0.25to0.50 0.50to0.75 0.75tol
R cnge of P eas on Correlation Coefficients
Correlations B etween Cabonyls ondPolaCompouncfc
Percent of Sites
-. — ' fO M t*> O3 J
D 01 O yi O
-------
Figure 8-2
Sum of the Geometric Means of the Concentrations of the Prevalent Carbonyls
oo
iu -
_>.
w O
re " "
Q
•*• Q
O ^~. "
Ew -9 7
Q. ' '
3 Q.
<*> ^ fi
£ o 5
"5 £
c tr 4
« g
« s
2S "
^° 2-
1 1
5
j
r -^
s
4 ^ o"}
*
^ * ^
'
" 5 -5-
i'.V * ^
** - v '•> !
» '(
"J^S
*3 f ' * f
<»•'«.
,*
§1?
"'
^ J-
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< "-* **
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•* "* # *" ~ t* ^i> * Ji> it <*•**' * x ^ j^
" > ^^i*" * *f S *• "#-f"'e- * ^ " ^.r * s* *
1 ^ V ^ ^ , ^ ^ ** ^ ^ 'v
EPTX CANJ BUVT RUVT GALA PARR BRVT B2LA BUND GRE/ UNVT HALA
Monitoring Location
-------
Figure 8-3
Comparison of BTEX Concentration Profiles to Carbonyl Compounds
B2LA
BRVT
BJND BUVT
Monitoring Site
CANJ
EPTX
QAcroleinmp-xylene HButyr/lsobutyrdctehycte:m.p-XYlene DBenzdctehyctemp-xylene
SAL A
GREY
HALA PARR
Monitoring Site
UNVT
EJAcroleinmp-xylene llButyr/lsobutyrddahyctemp-xylene DBenzddehydsmp-xylene
8-12
-------
Table 8-1
Summary of Pearson Correlations for Selected Meteorological Parameters and Measured Carbonyl Concentrations
Meteorological Parameter
Maximum Temperature*
Minimum Temperature*
Average Temperature*
Wind Speed*
Sea Level Pressure
Dew Point Temperature*
Visibility
Average Correlation
0.398 ±0.188
0.261 ±0.182
0.361 ±0.185
0.258 ± 0.082
-0.015 + 0.164
0.240 ±0.1 94
0.003 ±0.1 50
Site with Highest
Positive Correlation
(Value)
Beulah, ND
(0.681)
Beulah, ND
(0.618)
Beulah, ND (0.555 ±
0.378)
None
Hahnville, LA
(0.568)
Beulah, ND
(0.643)
Texarkana, AR
(0.349)
Site with Strongest
Negative Correlation
(Value)
Hahnville, LA
(-0.417)
Hahnville, LA
(-0.484)
Little Rock, AR (-0.339
±0.368)
Baton Rouge, LA
(-0.494)
Beulah, ND
(-0.344)
Hahnville, LA
(-0.457)
Hahnville, LA
(-0.551)
oo
* Statistically significant across the 12 sites.
-------
Table 8-2
Average Concentrations (ppbv) of Program-Wide Prevalent Carbonyls for the
1998 UATMP Compared to the Same Compounds for Previous Years
1994 1995
1996
1997
1998
B2LA
Acetaldehyde
Acetone
Butyr/Isobutryaldehyde
Formaldehyde
5.30
0.99
0.46
27.63
1.25
1.08
0.15
2.34
0.75
0.96
0.12
1.83
0.78
0.79
0.21
1.80
BRVT
Acetaldehyde
Acetone
Butyr/Isobutryaldehyde
Formaldehyde
2.60
0.78
0.21
' - 2.23
1.29
1.75
0.17"
2.74 "
0.86
1.36
0.12
1.93
0.76
1.10
0.14
1.74
BUND
Acetaldehyde
Acetone
Butyr/Isobutryaldehyde
Formaldehyde
-
-
-
0.64
1.30
0.11
1.36
rjBUYT ; . • .. v J
Acetaldehyde
Acetone
Butyr/Isobutryaldehyde
Formaldehyde
3.42
2.54
0.28
7.22
1.62
1.91
0.19
3.55
1.22
1.22
0.15
3.49
0.96
1.08
0.17
2.95
CANJ
Acetaldehyde
Acetone
Butyr/Isobutryaldehyde
Formaldehyde
0.52
0.71
0.04
1.75
2.05
1.30
0.19
9.14
1.59
1.69
0.23
3.84
1.88
1.95
0.57
3.66
EPTX
Acetaldehyde
Acetone
Butyr/Isobutryaldehyde
Formaldehyde
6.85
8.29
0.67
11.45
3.91
2.63
0.39
10.88
2.75
2.18
0.27
8.68
2.28
1.37
0.02
7.54
GALA
Acetaldehyde
Acetone
Butyr/Isobutryaldehyde
Formaldehyde
4.47
1.94
1.14
17.05
1.09
0.53
0.19
2.22
0.95
0.87
0.18
2.30
1.08
0.51
0.23
2.32
• Indicates compound was not included in the UATMP for that year.
8-14
-------
Table 8-2 (Continued)
Average Concentrations (ppbv) of Program-Wide Prevalent Carbonyls for the
1998 UATMP Compared to the Same Compounds for Previous Years
1994 1995
1996
1997
1998
GREY
Acetaldehyde
Acetone
Butyr/Isobutryaldehyde
Formaldehyde
-
-
-
0.70
0.95
0.10
1.64
HALA
Acetaldehyde
Acetone
B utyr/Isobutry al dehy de
Formaldehyde
5.50
2.20
1.13
- 27.20
1.65
0.98
0.25
3.20
1.15
0.85
0.23
3.46
0.67
0.62
0.15
1.72 '
PARR
Acetaldehyde
Acetone
Butyr/Isobutryaldehyde
Formaldehyde
-
-
0.83
1.03
0.15
3.10
0.81
1.23
0.14
1.80
RUVT
Acetaldehyde
Acetone
Butyr/Isobutryaldehyde
Formaldehyde
3.30
3.59
0.40
6.36
1.69
2.05
0.19
3.67
1.36
1.51
0.16
3.51
0.97
1.07
0.19
2.11
UNVT
Acetaldehyde
Acetone
Butyr/Isobutryaldehyde
Formaldehyde
0.82
0.81
0.03
0.98
0.77
1.09
0.09
2.39
0.81
1.17
0.12
4.97
0.46
0.90
0.12
1.06
- Indicates compound was not included in the UATMP for that year.
8-15
-------
Table 8-3
Comparison of Geometric Means of Program-Wide Prevalent Carbonyls with Total Air
Releases Reported by Facilities Within a 10-Mile Radius of UATMP Monitoring Stations
Acetaldehyde
Station
Code
CANJ
EPTX
GALA
RUVT
BUVT
PARR
B2LA
BRVT
GREY
BUND
HALA
ppbv
1.77
1.76
1.03
0.91
0.88
0.76
0.72
0.72
0.64
0.59
0.53
Ibs
0
0
0
0
0
0
2,241
0
73,951
0
10,815
Butyr/Isobutyraldehyde
Station
Code
CANJ
GALA
B2LA
EPTX
RUVT
BUVT
BRVT
PARR
UNVT
BUND
HALA
ppbv
0.51
0.15
0.15
0.15
0.14
0.12
0.12
0.09
0.08
0.08
0.07
Ibs
0
3,217
8
0
0
0
0
0
0
0
3,217
Formaldehyde
Station
Code
EPTX
CANJ
BUVT
GALA
RUVT
PARR
B2LA
BRVT
GREY
HALA
BUND
ppbv
5.26
3.36
2.72
2.14
1.90
1.62
1.59
1.57
1.34
1.27
1.19
Ibs
0
0
0
0
0
0
11,618
0
20,947
36,697
0
8-16
-------
Table 8-4
Ranking of Monitoring Stations by Levels of Total Program-Wide Prevalent Carbonyls
oo
Monitoring
Location
B2LA
BRVT
BUND
BUVT
CANJ
EPTX
GALA
GREY
HALA
PARR
RUVT
UNVT
Geometric Means of the
Total Program-Wide
Prevalent Carbonyls
Concentrations3
ppbv
1998
3.25
3.53
3.10
4.86
7.73
8.84
3.95
3.05
2.33
3.69
4.06
2.36
Cone.
Rank
8
7
9
3
2
1
5
10
12
6
4
11
Industrial Emissions of
Program-Wide Prevalent
Carbonyls within a 10-
Mile Radius of the
Monitoring Location6
Pounds in
1997
13,867
0
0
0
0
0
0
94,898
50,729
0
0
0
Emissions
Rank
3
4
4
4
4
4
3
1
2
4
4
4
t
Total Industrial Emissions
within a 10-Mile Radius of
the Monitoring Location0
Pounds in
1997
3,471,078
37,511
0
25,073
443,296
147,020
511,797
2,296,884
3,463,330
345,472
940
0
Emissions
Rank
1
•8
11
9
5
7
4
3
!z
,6
10
11
Total Number of Cars
Owned within a 10-Mile
Radius of the Monitoring
Locationd
Total Cars
256,716
22,611
5,616
86,381
1,503,540
360,257
45,196
70,410
60,821
124,765
22,848
23,650
Rank of
Total Cars
3
11
12
5
1
2
8
6
7
4
10
9
a This value was calculated as follows: (1) For each monitoring site, for each sampling event, the concentrations of the program-wide prevalent hydrocarbons
were summed. (2) For each monitoring site, the geometric mean of the sampling event totals was calculated.
bIndustrial emissions were calculated from emissions data for TRI reporting year 1997 (TRI, 1997). The emissions reported are the total air releases of the
halogenated hydrocarbons identified as program-wide prevalent for the 1998 UATMP. Acetone was not reportable to TRI in 1997.
c Industrial emissions were calculated from emissions data for TRI reporting year 1997 (TRI, 1997).
d The total number of cars owned within a 10-mile radius was estimated based on a ratio of 0.74 cars per person (U.S. population of 260,000,000 and total cars
in U.S. of 193,400,000). Information from "Statistical Abstract of the United States", 1999, and the internet link at http://link-usa.com/zipcode/pop.htm
-------
9.0 Data Quality
This section evaluates how precisely and accurately ambient air concentrations were
measured during the 1998 UATMP. As indicators of the reliability of experimental
measurements, both precision and accuracy should be considered when interpreting ambient air
monitoring results. In general, this section shows that the 1998 UATMP monitoring data are of a
known and high quality, particularly for the most program-wide prevalent compounds in urban
air.
9.1 Precision
Precision refers to the mutual agreement between independent measurements performed
according to identical protocols and procedures. To quantify "sampling and analytical precision"
(Le., how precisely the sampling and analytical methods measure ambient air concentrations), the
section then compares concentrations measured during analysis of duplicate samples.
,4%pliedio ambient air mottitoring,data,,precwqk is a measurement lofrandom,hrors (5> ^
-------
average concentration difference exceeds or nearly equals its central tendency, the
analytical method may not be capable of precisely characterizing annual concentrations.
Therefore, data interpretations for these compounds should be made with caution.
Relative percent difference (RPD) expresses average concentration differences relative to
the average concentrations detected during replicate analyses. The RPD is calculated as
follows:
IX, - X2 I
RPD = I ' _ 2 ' x 100 (1)
X
Where:
Xl is the ambient air concentration of a given compound measured in one sample;
X2 is the concentration of the same compound measured during replicate analysis; and
X is the arithmetic mean of X} and X2.
As Equation 1 shows, replicate analyses with low variability have lower RPDs (and better
precision), and replicate analyses with high variability have higher RPDs (and poorer precision).
The following approach was employed to estimate how precisely the central laboratory
analyzed 1998 UATMP samples:
RPDs and concentration differences were calculated for every replicate analysis performed
during the program. In cases where compounds were not detected during replicate
analyses, these parameters were not calculated.
Second, to make an overall estimate of method precision, program-average RPDs and
concentration absolute differences were calculated for each compound by averaging the
values from the individual replicate analyses.
Tables 9-1 and 9-2 use both absolute average concentration differences and RPDs to characterize
the analytical precision representing all sites for the VOC and carbonyl measurements made
during the 1998 UATMP, respectively.
9-2
-------
Replicate analytical data show that laboratory VOC analysis precision was excellent.
With the exception of acetylene (average concentration difference of 0.18 ppbv), average
concentration difference in replicate analyses was less than or equal to 0.07 ppbv. The method
was most precise when measuring air concentrations for the most program-wide prevalent
compounds (i.e., compounds consistently found at levels exceeding their detection limits). For
VOCs, samples exhibit RPDs ranging from 1 percent to 17 percent.
In terms of average concentration difference, the precision of the VOC analytical method
was fairly uniform across compounds, with few exceptions. The average concentration
difference during replicate analyses for most compounds was 0.03 ppbv or less, though acetylene
had a slightly greater concentration difference. The relatively high variability for acetylene
largely resulted from poor agreement in the replicate analysis of two sets of samples collected on
April 12, 1999, at El Paso, TX, and March 25, 1999, at Brattleboro, VT. Disregarding these
samples, the average concentration difference for acetylene becomes 0.11 ppbv, rather than
0.18 ppbv.
As Table 9-2 shows, laboratory analysis of carbonyl samples during the 1998 UATMP
was consistently more precise than analysis of VOC samples. The RPD was less than 20 percent
for every carbonyl compound. With one exception, the average concentration differences
observed upon replicate analyses of carbonyls were less than or equal to 0.01 ppbv—
formaldehyde had average concentration differences of 0.02 ppbv.
Accordingly, random errors during laboratory analysis had minimal impacts on the
carbonyl concentration data measured during the 1998 UATMP. Overall, replicate analyses of
both carbonyl and VOC samples suggest that the corresponding analytical methods consistently
measured each compound in air samples within a precision of 25 percent—a precision level well
within the UATMP data quality objectives (USEPA, 1988) and guidelines in the Compendium
Methods (USEPA, 1999).
9-3
-------
9.1.2 Sampling and Analytical Precision
As the name implies, sampling and analytical precision quantifies random errors
associated not only with analyzing ambient air samples in the laboratory but also with collecting
the samples in the field. This form of precision is most easily evaluated by comparing
concentrations measured in duplicate samples collected off the same manifold. During the 1998
UATMP, duplicate samples were collected on approximately 10 percent of the scheduled
sampling days, and most of these samples were analyzed in replicate. To calculate sampling and
analytical precision, data analysts first averaged the results from each replicate analysis (if
performed), then compared these average concentrations between the two samples in each
duplicate. Tables 9-3 and 9-4 present average concentration differences and RPDs as estimates of
sampling and analytical precision for VOC and carbonyl measurements, respectively. It should be
noted that Tables 9-1 and 9-2 are twice as high, representing the replicates of the duplicate
samples presented in Tables 9-3 and 9-4.
According to the sampling and analytical data in Table 9-3, concentrations of VOCs
measured in duplicate samples during the 1998 UATMP were in excellent agreement. On
average, these concentrations differed by 0.10 ppbv or less for almost every compound detected
during the program. With the exception of acetonitrile (RPD of 69 percent), RPDs ranged from
1 percent to 35 percent. The sampling and analytical precision data in Table 9-3 do not differ
significantly from the analytical precision data in Table 9-1. This similarity suggests that
limitations associated with laboratory analysis of the VOC samples during the 1998 UATMP
probably outweighed random errors associated with sampling procedures.
Like the duplicate sampling results for VOCs, the duplicate sampling results for carbonyls
were highly precise. As the data in Table 9-4 show, every carbonyl compound had an RPD for
sampling and analytical precision less than or equal to 20 percent. For most compounds, the
sampling and analytical RPDs (see Table 9-4) were notably higher than the analytical precision
RPDs (see Table 9-2)—a trend that differs from the trend observed for VOCs. This observation
suggests that random errors associated with collecting air samples and random errors associated
9-4
-------
with analyzing these samples both contributed significantly to overall imprecision in the carbonyl
sampling and analytical method. Random sampling errors most likely resulted from trace amounts
of carbonyls contaminating the silica gel sampling cartridges before the scheduled sampling days.
As the estimates of sampling and analytical precision show, however, such sources of
contamination did not have significant impacts—not greater than 0.20 ppbv, on average—on the
carbonyl monitoring results.
To summarize, duplicate sampling results indicate that the 1998 UATMP air quality
measurements generally have precision better than 25 percent—well within the UATMP data
quality objectives of 100 percent (USEPA, 1988). This excellent measurement precision suggests
that the 1998 UATMP monitoring data offer a precise account of air quality at the selected
monitoring locations, especially for the most program-wide prevalent compounds. Although
random errors had very small impacts on measurement of the less program-wide prevalent
compounds, participating agencies should note that the central tendencies for these compounds
have nearly the same magnitude as the average concentration difference. Therefore, central
tendency concentrations for these less program-wide prevalent compounds should be interpreted
with caution.
9.2 Accuracy
Highly accurate air sampling and analytical methods can measure air concentrations in
very close agreement to actual ambient levels. Laboratories typically evaluate their accuracy by
analyzing external audit samples and comparing measured concentrations to the known
concentrations within the audits.
„, ,.„•, • , > .,
indicates tne extent to which exr^ri^^
or "actuaP values. \ > , V \\>^ <"
~
9-5
-------
EPA/State participants provided three external audit samples for the 1998 UATMP. The
results are displayed on Table 9-5. All acceptance criteria were met representing accurate
carbonyl analytical methods.
The accuracy of the 1998 UATMP monitoring data can also be assessed qualitatively by
reviewing the accuracy of the monitoring methods and how they were implemented:
The sampling and analytical methods used in the 1998 UATMP (i.e., Compendium
Methods TO-11A and TO-15) have been approved by EPA for accurately measuring
ambient levels of VOCs and carbonyls, respectively—an approval that is based on many
years of research into the development of ambient air monitoring methodologies.
When collecting and analyzing ambient air samples, all field sampling staff and
laboratory analysts strictly followed quality control and quality assurance guidelines
detailed in the respective monitoring methods. This strict adherence to the well-
documented sampling and analytical methods suggests, though certainly does not prove,
that the 1998 UATMP monitoring data accurately represent ambient air quality.
9-6
-------
Table 9-1
VOC Analytical Precision
(Based on Replicate Analysis of 99 Valid Samples)
Compound
Number of
Observations
Average RPD in
Replicate
Analyses (%)
Average
Concentration
Difference in
Replicate
Analyses (ppbv)
lydrocarbons ,
Acetylene
Jenzene
,3-Butadiene
£thylbenzene
n-Octane
*ropylene
Styrene
Toluene
,2,4-Trimethylbenzene
,3,5-Trimethylbenzene
m-,p-Xylene
o-Xylene
99
99
54
99
95
99
98
99
99
99
99
99
10
5
18
8
13
6
17
7
11
15
8
10
0.18
0.03
0.03'
0.011
0.0 11
0.05
0.0 11
0.05
0.02'
0.01 '
0.03
0.01
lalogenated Hydrocarbons !
Jromochloromethane
Bromodichloromethane
Jromoform
Jromomethane
Carbon Tetrachloride
Chlorobenzene
Chloroethane
Chloroform
Chloromethane
Chloromethylbenzene
Chloroprene
Dibromochloromethane
0
0
0
6
99
0
0
2
99
0
8
1
NA
NA
NA
10
13
NA
NA
3
5
NA
0.4
NA
NA
NA
NA
<0.01'
0.011
NA
NA
<0.01'
0.03
NA
0.02
NA
9-7
-------
Table 9-1 (Continued)
VOC Analytical Precision
(Based on Replicate Analysis of 99 Valid Samples)
Compound
,2-Dibromoethane
w-Dichlorobenzene
o-Dichlorobenzene
>-Dichlorobenzene
,1-Dichloroethane
,2-Dichloroethane
,1-Dichloroethene
cis- 1 ,2-Dichloroethylene
trans- 1 ,2-Dichloroethylene
,2-Dichloropropane
cis- 1 ,3-Dichloropropene
trans- 1 ,3-Dichloropropene
)ichlorodifluoromethane
)ichlorotetrafluoroethane
lexachloro- 1 ,3-Butadiene
Methylene Chloride
, 1 ,2,2-Tetrachloroethane
Petrachloroethylene
1 ,2,4-Trichlorobenzene
L,l,l-Trichloroethane
1 , 1 ,2-Trichloroethane
Trichloroethylene
rrichlorofluoromethane
rrichlorotrifluoroethane
Vinyl Chloride
Number of
Observations
1
0
1
13
0
0
0
1
0
0
0
0
99
9
1
96
0
39
2
99
0
10
99
98
0
Average RPD in
Replicate
Analyses (%)
NA
NA
NA
6
NA
NA
NA
NA
NA
NA
NA
NA
5
3
NA
16
NA
14
NA
13
NA
8
15
9
NA
Average
Concentration
Difference in
Replicate
Analyses (ppbv)
NA
NA
NA
<0.01'
NA
NA
NA
NA
NA
NA
NA
NA
0.03
<0.01'
NA
0.031
NA
0.011
NA
0.011
NA
0.01'
0.07
0.011
NA
9-8
-------
Table 9-1 (Continued)
VOC Analytical Precision
(Based on Replicate Analysis of 99 Valid Samples)
Compound
Number of
Observations
Average RPD in
Replicate
Analyses (%)
Average
Concentration
Difference in
Replicate
Analyses (ppbv)
^lar Compounds
Acetonitrile
Acrylonitrile
Ethyl Acrylate
Ethyl tert-Butyl Ether
Methyl Ethyl Ketone
Methyl Isobutyl Ketone
Vlethyl Methacrylate
Methyl tert-Butyl Ether
tert-Amyl Methyl Ether
47
4
0
0
99
16
0
48
8
10
8
NA
NA
9
1
NA
5
1
1.08
0.041
NA
NA
0.05
<0.01'
NA
0.05
0.01'
'The average concentration for these compounds is less than 5 times the current Method Detection Limits.
Notes: NA = Not applicable. (Precision cannot be evaluated for compounds that were not detected in any of the replicate
analyses.)
"Number of observations" equals the number of replicate analyses in which the compound was detected.
Program-wide prevalent compounds are shown in bold font. As discussed in Section 9.1.1, these compounds generally
had better analytical precision than the compounds less program-wide prevalent in ambient air (i.e., the compounds in
plain font).
9-9
-------
Table 9-2
Carbonyl Analytical Precision
(Based on Replicate Analysis of 64 Valid Samples)
Compound
Acetaldehyde
Acetone
Acrolein
Jenzaldehyde
Butyr/Isobutyraldehyde
Crotonaldehyde
2,5-Dimethylbenzaldehyde
formaldehyde
iexaldehyde
sovaleraldehyde
'ropionaldehyde
^olualdehydes
Valeraldehyde
Number of
Observations
64
64
29
61
60
37
2
64
64
23
46
52
62
Average RPD in
Replicate
Analyses (%)
1
1
19
13
5
11
3
2
13
23
4
19
9
Average
Concentration
Difference in
Replicate
Analyses (ppbv)
0.01
0.01
<0.01
<0.01
0.01
<0.01
<0.01'
0.02
<0.01
0.01
0.01
<0.01
<0.01
'The average concentration for these compounds is less than 5 times the current Method Detection Limits.
Notes: "Number of observations" equals the number of replicate analyses in which the compound was detected.
Compounds with program-wide prevalence greater than 75 percent are shown in bold font. As discussed in
Section 9.1.1, the analytical precision for these compounds was similar to the analytical precision for compounds less
program-wide prevalent in ambient air (i.e., the compounds in plain font).
9-10
-------
Table 9-3
VOC Sampling and Analytical Precision
(Based on 50 Valid Duplicate Samples)
Compound
Number of
Observations
Average RPD in
Replicate
Analyses of
Duplicates (%)
Average
Concentration
Difference in
Replicate
Analyses of
Duplicates
(ppbv)
•tydrocarbons
Acetylene
Benzene
1 ,3-Butadiene
Lthylbenzene
i-Octane
'ropylene
Styrene
Toluene
, 2 ,4-Tr imethylbenzene
,3 ,5-Trimethylbenzene
n-,/?-Xylene
0-Xylene
50
50
25
50
48
50
50
50
50
50
50
50
5
6
19
8
15
8
24
10
12
13
8
10
0.07
0.02
0.03 '
0.01
0.01 '
0.05
0.03
0.05
0.03 '
0.01 '
0.03
0.02
ialogenated Hydrocarbons
Jromochloromethane
komodichloromethane
Bromoform
Bromomethane
Carbon Tetrachloride
Chlorobenzene
Chloroethane
Chloroform
^hloromethane
Chloromethylbenzene
Chloroprene
0
0
0
3
50
0
0
1
50
0
4
NA
NA
NA
1
25
NA
NA
NA
12
NA
4
NA
NA
0.00
<0.01'
0.021
NA
NA
NA
0.08
NA
0.04
9-11
-------
Table 9-3 (Continued)
VOC Sampling and Analytical Precision
(Based on 50 Valid Duplicate Samples)
Compound
)ibromochloromethane
,2-Dibromoethane
w-Dichlorobenzene
9-Dichlorobenzene
r-Dichlorobenzene
, 1 -Dichloroethane
,2-Dichloroethane
,1-Dichloroethene
cis-l ,2-Dichloroethylene
trans- 1 ,2-Dichloroethylene
1 ,2-Dichloropropane
cis- 1 ,3-Dichloropropene
trans- 1 ,3-Dichloropropene
Dichlorodifluoromethane
)ichlorotetrafluoroethane
lexachloro- 1 ,3-Butadiene
Methylene Chloride
1 , 1 ,2,2-Tetrachloroethane
Petrachloroethylene
[ ,2,4-Trichlorobenzene
1,1,1-Trichloroethane
1 , 1 ,2-Trichloroethane
Irichloroethylene
rrichlorofluoromethane
Frichlorotrifluoroethane
Number of
Observations
0
1
0
0
7
0
0
0
0
0
0
0
0
50
4
0
46
0
20
1
50
0
4
50
50
Average RPD in
Replicate
Analyses of
Duplicates (%)
r NA
NA
NA
NA
7
NA
NA
NA
NA
NA
NA
NA
NA
6
16
NA
35
NA
23
NA
12
NA
4
30
10
Average
Concentration
Difference in
Replicate
Analyses of
Duplicates
(ppbv)
NA
NA
NA
NA~
0.011
NA
NA
NA
NA
NA
NA
NA
NA
0.04
<0.01'
NA
0.081
0.00
0.021
NA
0.011
NA
0.0 11
0.15
0.011
9-12
-------
Table 9-3 (Continued)
VOC Sampling and Analytical Precision
(Based on 50 Valid Duplicate Samples)
Compound
Vinyl Chloride
Number of
Observations
0
Average RPD in
Replicate
Analyses of
Duplicates (%)
NA
Average
Concentration
Difference in
Replicate
Analyses of
Duplicates
(ppbv)
NA
^lar Compounds
Acetonitrile
Acrylonitrile
ithyl Acrylate
Ethyl tert-Butyl Ether
Methyl Ethyl Ketone
Vlethyl Isobutyl Ketone
Methyl Methacrylate
Methyl tert-Butyl Ether
tert-Amyl Methyl Ether
21
2
0
0
44
5
0
25
4
69
NA
NA
NA
23
1
NA
12
15
2.76
<0.01'
NA
NA
0.12
0.01 '
NA
0.06
0.02'
'The average concentration for these compounds is less than 5 times the current Method Detection Limits.
Notes: NA = Not applicable. (Precision cannot be evaluated for compounds that were not detected in any of the duplicate
samples.)
"Number of observations" equals the number of duplicate samples in which the compound was detected.
Program-wide prevalent compounds are shown in bold font. As discussed in Section 9.1.2, these compounds generally
had better sampling and analytical precision than the compounds less program-wide prevalent in ambient air (i.e., the
compounds in plain font).
9-13
-------
Table 9-4
Carbonyl Sampling and Analytical Precision
(Based on 32 Valid Duplicate Samples)
Compound
Acetaldehyde
Acetone
Acrolein
3enzaldehyde
Jutyr/Isobutyraldehyde
Crotonaldehyde
2,5-Dimethylbenzaldehyde
Formaldehyde
Hexaldehyde
sovaleraldehyde
'ropionaldehyde
Tolualdehydes
Valeraldehyde
Number of
Observations
32
32
14
30
30
17
1
32
31
9
32
25
31
Average RPD in
Replicate
Analyses of
Duplicates (%)
14
20
16
20
18
25
1
14
22
21
14
24
19
Average
Concentration
Difference in
Replicate
Analyses of
Duplicates (ppbv)
0.07
0.22
<0.01
0.01
0.01
0.01
<0.01'
0.17
0.01
0.01
0.01
0.01
0.01
'The average concentration for these compounds is less than 5 times the current Method Detection Limits.
Notes: "Number of observations" equals the number of replicate analyses in which the compound was detected.
Compounds with program-wide prevalence greater than 75 percent are shown in bold font. As discussed in
Section 9.1.2, the analytical precision for these compounds was similar to the analytical precision for compounds less
program-wide prevalent in ambient air (i.e., the compounds in plain font).
9-14
-------
Table 9-5
1999 Carbonyl Audit Results
Audit
Date
05/14/99
08/06/99
10/07/99
Compound
Formaldehyde
Acetaldehyde
Acetone
Formaldehyde
Acetaldehyde
Acetone
Formaldehyde
Acetaldehyde
Acetone
Sample ID
1199
2199
3199
1199
2199
3199
1199
2199
3199
1299
2299
3299
1299
2299
3299
1299
2299
3299
1399
2399
3399
1399
2399
3399
1399
2399
3399
Concentration (ug/cartridge)
Reported
0.05
1.05
3.44
0.03
0.87
2.62
0.07
1.22
3.95
0.05
0.93
4.32
0.04
1.57
4.20
0.12
1.13
3.05
0.02
1.60
3.15
0.05
0.96
4.82
0.24
1.51
4.49
Actual
0.00
1.25
4.00
0.00
1.00
3.00
0.00
1.40
4.50
0.00
0.90
4.25
0.00
1.50
4.00
0.00
1.00
3.00
0.00
1.50
3.00
0.00
0.85
4.50
0.00
1.20
4.00
%
Difference
blank
-20.0
-15.3
blank
-16.0
-13.7
blank
-17.9
-13.8
blank
-2.2
0.5
blank
2.0
4.0
blank
1.0
-2.3
blank
5.3
4.3
blank
7.1
6.0
blank
5.8
6.3
Passed/Failed
Passed
Passed
Passed
- - - mr
Passed
Passed
Passed
Passed
Passed
Passed
9-15
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10.0 Conclusions and Recommendations
As indicated throughout this report, UATMP monitoring data offer a wealth of
information for evaluating trends and patterns in air quality and should ultimately help a wide
range of audiences understand the complex nature of urban air pollution. The following
discussion summarizes the main conclusions of this report and presents recommendations for
ongoing urban air monitoring efforts.
10.1 Conclusions
Analyses of the 1998 UATMP monitoring data identified the following notable trends
and patterns in urban air pollution:
Ambient air concentrations of hydrocarbons. Levels of airborne hydrocarbons were
highest at the El Paso, TX, monitoring location and were lowest at the Underhill, VT, and
Beulah, ND, monitoring locations. At most stations, emissions from motor vehicles and
industrial sources appear to be important sources of hydrocarbons in ambient air.
Ambient air concentrations of halogenated hydrocarbons. Unlike the concentration
range seen for the hydrocarbons, little variation is demonstrated for the concentrations
and no strong trends are exhibited in 1998 UATMP halogenated hydrocarbons data. No
single factor was identified to explain air quality trends for this group of compounds.
Ambient air concentrations of polar compounds. Levels of airborne polar compounds
were significantly higher at the Baton Rouge, LA, monitoring location while the
remaining sites demonstrated little variation in polar compound concentrations. The TRI
emissions ranks for the 12 sites were very consistent with the respective rank of the total
ambient air concentration of the program-wide prevalent polar compounds. However,
before drawing conclusions on the impact of industrial emissions and ambient air
concentrations, it should be noted that 6 of the 12 monitoring sites did not report any
industrial emissions of program-wide prevalent polar compounds.
Ambient air concentrations ofcarbonyls. The UATMP monitoring data seem to suggest
that emissions from motor vehicles and photochemical reactions most strongly influence
ambient air concentrations of carbonyls. The fact that ambient air concentrations of most
carbonyls were positively correlated with temperature at most monitoring locations
supported the hypothesis that photochemical reactions form carbonyls in ambient air.
Although emissions data from facilities subject to the Toxic Release Inventory reporting
requirements were quite inconsistent with the observed spatial variations in
10-1
-------
concentrations of carbonyls, emissions from other industrial emissions sources may have
contributed to the levels of carbonyls detected during the UATMP.
10.2 Recommendations
In light of the lessons learned from the 1998 UATMP, a number of recommendations for
future ambient air monitoring are warranted:
Continue to identify and implement improvements to the sampling and analytical
methods. The improvements made to the analytical methods prior to the 1998 UATMP
allowed for measurement of ambient air concentrations of 11 compounds that were not
measured during previous programs. This improvement provides sponsoring agencies
and a variety of interested parties with important information about air quality within
their urban areas. Further research is encouraged to identify other method improvements
that would allow the UATMP to characterize an even wider range of components in
urban air pollution.
Continue to strive to develop standard conventions for interpreting air monitoring data.
The lack of consistent approaches to present and summarize ambient air monitoring data
complicates or invalidates comparisons between different studies. Additional research
should be conducted on the feasibility of establishing standard approaches for analyzing
and reporting air monitoring data.
Prepare a report characterizing all years of the UATMP and then update it yearly to
better assess Trends and better understand the nature of U.S. urban air pollution.
Consider more rigorous study of the impact of automobile emissions on ambient air
quality using the complete UATMP data set. Because the UATMP has monitoring sites
where years of continuous data are collected, a real opportunity exists to evaluate the
importance and impact of automobile emissions on ambient air quality. Suggested areas
of study include:
1. Signature Compound Assessment. Sample data from each site should be
evaluated to look for signature compounds from mobile sources—that is, species
typically associated with only diesel and/or gasoline combustion. If the
appropriate compounds are included in the UATMP speciation, sites lacking these
compounds can be excluded from subsequent analyses. Desert Research Institute
can provide a listing of potential signature compounds for mobile sources.
2. Micro-Climate Assessment. An assessment is needed of the immediate
micro-climate for a representative "urban" and "rural" site, to determine a
reasonable geographic radius of influence. It is absolutely critical to determine a
10-2
-------
rough estimate of the maximum radius of concern (Rmax) in order to know what
sources need to be included in the characterization. A value for Rmax may be
determined with relatively little effort using simple dispersion models, such as
CALINZ4 for urban settings. In these models Rmax would be defined for non-
reactive species such as CO or PM. Since most/all of the toxic compounds of
concern have some level of reactivity, Rmax would actually be somewhat less.
Therefore this method would provide a conservative estimate for Rmax.
3. Identify Roadways of Concern. All roadways within a distance of Rmax should be
identified for each site. Local area maps are best suited for this purpose.
4. Estimate Traffic Volumes. Data from the Highway Performance Monitoring
System (HPMS) or the Bureau of Transportation Statistics could be used to
estimate annual average traffic counts, as well as the split between gasoline and
diesel vehicles, for interstate and other major highways. Local transportation
planning organizations should be able to provide counts for other urban roads.
Rural non-interstate roads will probably require qualitative assessment, based on
local resident estimates or short-duration observation. Note that obtaining the
precise split between gasoline and diesel vehicles for any given roadway is a
lower priority - national default values could be used instead.
5. Parking Lot Characterizations. Several monitoring locations are situated in or
near parking lots. Evaporative emissions from parked gasoline vehicles could
have a very significant impact on the monitors for these sites (depending upon the
species of concern). Therefore we recommend determining the size of the lots in
question in terms of number of spaces, as well as an average occupancy rate with
total vehicles per day (to determine the number of start episodes). The occupancy
rate should be a 24 hour annual average, and can be established either through
observation or local "experts" (e.g., the lot operator). Also, it should be
determined if the parking is covered or open—covered lots can significantly
decrease crankcase temperatures and therefore lower evaporative emissions rates.
6. Site-Specific Information. Additional information could be collected as needed to
improve the quality of discussions of air quality at specific sites. For example, for
the El Paso site the UATMP could obtain a vehicle count split for US versus
Mexican vehicles. Mexican vehicles have dramatically higher pollution rates and
should be considered separately. This estimate could be obtained from the EPA
or Texas Natural Resource Conservation Commission Border Liaisons.
Encourage continued participation in the UATMP. Ongoing ambient air monitoring at
fixed locations can provide insight into long-term trends in urban air quality and the
potential for urban air pollution to cause adverse health effects among the general
population. Therefore, state and local agencies should be strongly encouraged either to
develop and implement their own ambient air monitoring programs or to participate in
future UATMP monitoring efforts.
10-3
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11.0 References
ATSDR, 1993. "lexicological Profile for Methylene Chloride." U.S. Department of Health &
Human Services, Agency for Toxic Substances and Disease Registry. April, 1993.
ATSDR, 1994. "Toxicological Profile for Carbon Tetrachloride." U.S. Department of Health &
Human Services, Agency for Toxic Substances and Disease Registry. September, 1997.
ATSDR, 1995. "Toxicological Profile for 1,1,1 -Trichloroethane." U.S. Department of Health &
Human Services, Agency for Toxic Substances and Disease Registry. August, 1995.
ATSDR, 1997a. "Toxicological Profile for Chloromethane." U.S. Department of Health &
Human Services, Agency for Toxic Substances and Disease Registry. September, 1997.
ATSDR, 1997b. "Toxicological Profile for Tetrachloroethylene." U.S. Department of Health &
Human Services, Agency for Toxic Substances and Disease Registry. September, 1997.
Conner, et al., 1995. "Transportation-Related Volatile Hydrocarbon Source Profiles Measured in
Atlanta." Teri L. Conner, William A. Lonneman, Robert L. Seila. Journal of the Air and
Waste Management Association, 45: 383-394. 1995.
ERG, 1997. "1995 Urban Air Toxics Monitoring Program - Final Report." Eastern Research
Group. Prepared for U.S. Environmental Protection Agency, Office of Air Quality
Planning and Standards. January, 1997.
Fujita, et al., 19,94. "Validation of the Chemical Mass Balance Receptor Model Applied to
Hydrocarbon Source Apportionment in the Southern California Air .Quality Study." Eric
M. Fujita, John G. Watson, Judith C. Chow, and Zhiqiang Lu. Environmental Science
and Technology, 28:1633-1649. 1994.
Gilbert, 1987. "Statistical Methods for Environmental Pollution Monitoring." Richard O.
Gilbert. Van Nostrand Reinhold Publishers. 1987.
Godish, 1997. "Air Quality." Thad Godish. Lewis Publishers. 1997.
Graedel, 1978. "Chemical Compounds in the Atmosphere." T.E. Graedel. Academic Press.
1978.
Harnett, 1982. "Statistical Methods." Donald L. Harnett, Addison-Wesley Publishing Company,
Third Edition. 1982.
11-1
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Radian, 1990. "1989 Urban Air Toxics Monitoring Program - Final Report." Radian
Corporation. Prepared for U.S. Environmental Protection Agency, Office of Air Quality
Planning and Standards. September, 1990.
Radian, 1991. "1990 Urban Air Toxics Monitoring Program - Final Report." Radian
Corporation. Prepared for U.S. Environmental Protection Agency, Office of Air Quality
Planning and Standards. June, 1991.
Radian, 1996. "1994 Urban Air Toxics Monitoring Program - Final Report." Radian
Corporation. Prepared for U.S. Environmental Protection Agency, Office of Air Quality
Planning and Standards. June, 1996.
Ramamoorthy and Ramamoorthy, 1997. "Chlorinated Organic Compounds in the Environment:
Regulatory and Monitoring Assessment." Sub Ramamoorthy and Sita Ramamoorthy.
Lewis Publishers. 1997.
Scheff, 1993. "Receptor Modelling of Volatile Organic Compounds. 1. Emission Inventory and
Validation." Peter A. Scheff and Richard A. Wadden. Environmental Science and
Technology, 27: 617-625. 1993.
Seinfeld, 1986. "Atmospheric Chemistry and Physics of Air Pollution." John H. Seinfeld. John
Wiley & Sons, Inc. 1986.
TRI, 1997. 1997 Toxic Release Inventory 1987 - 1997 CD-ROM. U.S. Environmental
Protection Agency, Office of Pollution Prevention and Toxics. August, 1997.
USDOC, 1993. "1990 Census of Population and Housing." U.S. Department of Commerce,
Bureau of the Census. July, 1993.
USEPA, 1986. "Guideline on Air Quality Models." U.S. Environmental Protection Agency,
Office of Air and Radiation, Office of Air Quality Planning and Standards. July, 1986.
USEPA, 1988. "Data Quality Objectives for the Urban Air Toxics Monitoring Program (Stages I
and II)." U.S. Environmental Protection Agency, Office of Air and Radiation, Office of
Air Quality Planning and Standards. June, 1988.
USEPA, 1995. "Toxic Chemical Release Inventory Reporting Form R and Instructions."
Revised 1994 Version. U.S. Environmental Protection Agency, Office of Pollution
Prevention and Toxics. March, 1995.
USEPA, 1997. "National Air Pollutant Emission Trends, 1900- 1996." U.S. Environmental
Protection Agency, Office of Air and Radiation, Office of Air Quality Planning and
Standards. December, 1997.
11-2
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USEPA, 1997a. "Toxics Release Inventory 1987-1995 CD-ROM." United States
Environmental Protection Agency, Office of Pollution Prevention and Toxics. EPA
749-C-97-003. August, 1997.
USEPA, 1999. "Compendium Method TO-11A: Determination of Formaldehyde in Ambient
Air Using Adsorbent Cartridge Followed by High Performance Liquid Chromatography
(HPLC)." U.S. Environmental Protection Agency, Center for Environmental Research
and Information. EPA/625/R-96/010b. January, 1999.
USEPA, 1999. "Compendium Method TO-15: Determination of Volatile Organic Compounds
(VOC) in Ambient Air Collected in Specially-Prepared Canisters and Analyzed by Gas
Chromatography/Mass Spectrometry (GC/MS)." U.S. Environmental Protection Agency,
Center for Environmental Research and Information. EPA/625/R-96/010b.
January, 1999.
11-3
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APPENDIX A
AIRS SITE DESCRIPTIONS FOR THE
1998 UATMP MONITORING STATIONS
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05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
State: 05 ARKANSAS AQCR: 022 SHREVEPORT-TEXARKANA-TYLE
County: 091 MILLER MSA : 8360 TEXARKANA, TX-TEXARKANA,
Site : 0096 CMSA: 0000 DESCRIPTION UNKNOWN
Elevation (MSL) : METERS Date Established: 97/08/01
Land Use :1 RESIDENTIAL Date Last Updated: 99/01/20
Location Setting : 3 RURAL Date Terminated : / /
City : 00000 NOT IN A CITY
Latitude :+33:11:15:0000 Longitude :-94:01:26:0000
Method of Determ.: NA V-GPS Est. of Accuracy : 0.1OOOOMIN
Datum : 00 DATUM UNKNOW Scale : NA
UTM= Zone: 15 Easting: 404563 Northing: 3672330
Address : ROUTE 1, TEXARKANA
Support Agency : 001 ARKANSAS DEPARTMENT OF ENVIRONMENTAL QUALITY
Location Descrip.:
GREY SITE
05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
Site-Id : 05-091-0096 State or Local Site Id:
SiteLoc. MSA CMSA
Type Description Rep. Rep.
Tangent Street Type Direction Traffic Flow Street Name
Number Road To Street Flow Year
1 6 NE 5 1998 MILLER CO. 28
05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
Site-Id : 05-091-0096
Met-Site-Id.: - - Direction: Type: 1 Distance: 0 METERS
Open Land Direction Max.Beam Min.Beam Receiver Transmitter Beam
Path# Use To Trans. Height Height Height Height Length
( METERS —)
COMMENTS:
-------
05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
State : 05 ARKANSAS AQCR: 016 CENTRAL ARKANSAS
County: 119 PULASKI MSA : 4400 LITTLE ROCK-NORTH LITTLE
Site : 0007 CMSA: 0000 DESCRIPTION UNKNOWN
Elevation (MSL) : 80 METERS Date Established : 86/04/01
Land Use :2 COMMERCIAL Date Last Updated: 99/02/08
Location Setting : 1 URBAN AND CE Date Terminated : / /
City : 50450 NORTH LITTLE ROCK
Latitude :+34:45:22:0000 Longitude :-92:16:33:0000
Method of Determ.: Est. of Accuracy :
Datum : Scale :
UTM= Zone: 15 Easting: 566279 Northing : 3846039
Address : PIKE AVE AT RIVER ROAD
Support Agency : 002 ARKANSAS DEPARTMENT OF ENVIRONMENTAL QUALITY
Location Descrip.:
05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
Site-Id : 05-119-0007 State or Local Site Id:
SiteLoc. MSA CMSA
Type Description Rep. Rep.
Tangent Street Type Direction Traffic Flow Street Name
Number Road To Street Flow Year
1 6 500
05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
Site-Id: 05-119-0007
Met-Site-Id.: - - Direction: Type: Distance: 0 METERS
Open Land Direction Max.Beam Min.Beam Receiver Transmitter Beam
Path# Use To Trans. Height Height Height Height Length
( METERS )
COMMENTS: SITE NAME PARR RECLOATION OF SLAMS MID-TOWN SITE
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05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
State : 22 LOUISIANA AQCR: 106 SOUTHERN LOUIS IAN A-SOUTHE
County: 033 EAST BATON ROUGE MSA : 0760 BATON ROUGE, LA
Site : 0009 CMSA: 0000 DESCRIPTION UNKNOWN
Elevation (MSL) : 62 METERS Date Established : 92/08/01
Land Use :2 COMMERCIAL Date Last Updated: 99/01/13
Location Setting : 1 URBAN AND CE Date Terminated : / /
City : 05000 BATON ROUGE
Latitude :+30:27:40:0000 Longitude :-91:10:37:0000
Method of Determ.: Est. of Accuracy :
Datum : Scale :
UTM = Zone : 15 Easting : 675028 Northing : 3371143
Address : 1071 LEESVILLEAVE
Support Agency : 001 STATE OF LOUISIANA
Location Descrip.:
05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
Site-Id : 22-033-0009 State or Local Site Id:
SiteLoc. MSA CMSA
Type Description Rep. Rep.
Tangent Street Type Direction Traffic Flow Street Name
Number Road To Street Flow Year
1 6 5000
05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
Site-Id : 22-033-0009
Met-Site-Id.: - - Direction: Type: Distance: 0 METERS
Open Land Direction Max.Beam Min.Beam Receiver Transmitter Beam
Path# Use To Trans. Height Height Height Height Length
( METERS )
COMMENTS: CAPITOL SITE - RELOCATE FOR 220330006
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05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
State : 22 LOUISIANA AQCR: 106 SOUTHERN LOUIS IAN A-SOUTHE
County: 089 ST CHARLES MSA : 5560 NEW ORLEANS, LA
Site : 0003 CMSA: 0000 DESCRIPTION UNKNOWN
Elevation (MSL) : 3 METERS Date Established : 91/03/01
Land Use :3 INDUSTRIAL Date Last Updated: 99/01/13
Location Setting : 3 RURAL Date Terminated : / /
City :32510HAHNVILLE
Latitude :+29:59:03:0000 Longitude :-90:24:38:0000
Method of Determ.: Est. of Accuracy :
Datum : Scale :
UTM = Zone : 15 Easting : 749833 Northing : 3319674
Address : 1 RIVER PARK DRIVE
Support Agency : 001 STATE OF LOUISIANA
Location Descrip.:
05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
Site-Id : 22-089-0003 State or Local Site Id:
SiteLoc. MSA CMSA
Type Description Rep. Rep.
Tangent Street Type Direction Traffic Flow Street Name
Number Road To Street Flow Year
05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
Site-Id: 22-089-0003
Met-Site-Id.: - - Direction: Type: Distance: 0 METERS
Open Land Direction Max.Beam Min.Beam Receiver Transmitter Beam
Path* Use To Trans. Height Height Height Height Length
( METERS )
COMMENTS: RIVER PARK APARTMENT
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05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
State : 22 LOUISIANA AQCR: 106 SOUTHERN LOUISIANA-SOUTHE
County: 095 ST JOHN THE BAPTIST MSA : 5560 NEW ORLEANS, LA
Site : 0002 CMSA: 0000 DESCRIPTION UNKNOWN
Elevation (MSL) : 9 METERS Date Established : 71/01/01
Land Use :3 INDUSTRIAL Date Last Updated: 99/03/05
Location Setting : 3 RURAL Date Terminated : / /
City : 00000 NOT IN A CITY
Latitude :+30:03:30:0000 Longitude :-90:36:30:0000
Method of Determ.: Est. of Accuracy :
Datum : Scale :
UTM= Zone: 15 Easting: 730573 Northing: 3327480
Address : AZALEA AND SOUTH APRICOT STREET
Support Agency : 000 DESCRIPTION UNKNOWN
Location Descrip.:
05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
Site-Id : 22-095-0002 State or Local Site Id:
SiteLoc. MSA CMSA
Type Description Rep. Rep.
Tangent Street Type Direction Traffic Flow Street Name
Number Road To Street Flow Year
05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
Site-Id : 22-095-0002
Met-Site-Id.: - - Direction: Type: Distance: 0 METERS
Open Land Direction Max.Beam Min.Beam Receiver Transmitter Beam
Path# Use To Trans. Height Height Height Height Length
( METERS )
COMMENTS: SITE ACTIVATED FOR SULFUR DIOXIDE IN 1973 A LARGE REFINERY
IS LOCATING IN THE AREA IN 1975 SULFUR DIOXIDE VAL REPRESENT BACKGR D
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05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
State : 34 NEW JERSEY AQCR: 045 METROPOLITAN PHILADELPHIA
County: 007 CAMDEN MSA : 6160 PHILADELPHIA, PA-NJ
Site : 0003 CMSA: 0077 PHIL-WIL-AT.C,PA-NJ-DE-MD
Elevation (MSL) : 6 METERS Date Established : 68/01/01
Land Use :l RESIDENTIAL Date Last Updated: 99/01/13
Location Setting : 2 SUBURBAN Date Terminated : / /
City :i 0000 CAMDEN
Latitude : +39:55:22:0000 Longitude : - 75:05:50:0000
Method of Determ.: Est. of Accuracy :
Datum : Scale :
UTM= Zone: 18 Easting: 491692 Northing : 4419012
Address : COPEWOOD E. DAVIS STS; TRAILER
Support Agency : 001 NEW JERSEY STATE DEPARTMENT OF ENVIRONMENTAL
PROTECTIO
Location Descrip.:
05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
Site-Id : 34-007-0003 State or Local Site Id:
SiteLoc. MSA CMSA
Type Description Rep. Rep.
Tangent Street Type Direction Traffic Flow Street Name
Number Road To Street Flow Year
1 4 E 45000 1986 ROUTE 130
2 5 NE 14000 1986 HADDON AVENUE
3 6 3000
05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
Site-Id : 34-007-0003
Met-Site-Id.: - - Direction: Type: 1 Distance: 0 METERS
Open Land Direction Max.Beam Min.Beam Receiver Transmitter Beam
Path* Use To Trans. Height Height Height Height Length
( METERS )
COMMENTS: NJ #04081, START SO2,O3,1/1/68,NJ #058(TSP)START 9/3/83, SO4 10/83
START IP #2 10/83,SSI,SLAMS-TSP,CO 10/1/84;TSP DISC. 12/31/86
-------
PF8 INVALID - END OF SELECTED RECORDS
02/14/00 AIRS Air Quality Subsystem AMP510SB
Browse Site Data Page 1/3
State : 38 NORTH DAKOTA AQCR: 172 NORTH DAKOTA
County: 057 MERCER MSA : 0000 NOT IN AN MSA
Site : 0004 CMSA: 0000 DESCRIPTION UNKNOWN
Elevation (MSL) : 630 METERS Date Established : 98/12/13
Land Use :4 AGRICULTURAL Date Last Updated: 99/06/15
Location Setting : 3 RURAL Date Terminated : / /
City : 00000 NOT IN A CITY
Latitude :+47:17:55:0000 Longitude :-101:46:01:0000
Method of Determ.: SUR-GPS Est. of Accuracy : 0.01000SEC
Datum : 00 DATUM UNKNOW Scale : NA
UTM= Zone: 14 Easting: 290816 Northing : 5241843
Address : BEULAH NORTH
Support Agency : 001 NORTH DAKOTA STATE DEPARTMENT OF HEALTH
Location Descrip.:
LICATED IN A WILDLIFE MANAGEMENT AREA
PF3=end PF4=main menu PF5=terminate PF7=prev PF8=next PF9=gen
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12/07/98 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
State : 48 TEXAS AQCR: 153 EL PASO-LAS CRUCES-ALAMOG
County: 141 EL PASO MSA : 2320 EL PASO, TX
Site : 0027 CMSA: 0000 DESCRIPTION UNKNOWN
Elevation (MSL) : 1140 METERS Date Established : 73/01/01
Land Use :2 COMMERCIAL Date Last Updated: 98/09/25
Location Setting : 1 URBAN AND CE Date Terminated : / /
City : 24000 EL PASO
Latitude : +31:45:45:0000 Longitude : -106:29:13:0000
Method of Determ.: Est. of Accuracy :
Datum : Scale :
UTM= Zone: 13 Easting: 359179 Northing : 3514886
Address : 500 NORTH CAMPBELL ST.
Support Agency : 001 TEXAS NATURAL RESOURCES CONSERVATION COMMISSION
Location Descrip.:
12/07/98 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
Site-Id : 48-141-0027 State or Local Site Id:
SiteLoc. MSA CMSA
Type Description Rep. Rep.
1 UPWIND BACKGROUND 2320
Tangent Street Type Direction Traffic Flow Street Name
Number Road To Street Flow Year
1 5 S 20000 1979 CAMPBELL STREET
2 4 SE 25000 1979 FRANKLIN STREET
3 4 NW 25000 1979 MISSOURI STREET
4 3 NE 160040 1992 ffl-10
12/07/98 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
Site-Id: 48-141-0027
Met-Site-Id.: - - Direction: Type: Distance: 0 METERS
Open Land Direction Max.Beam Min.Beam Receiver Transmitter Beam
Path# Use To Trans. Height Height Height Height Length
( METERS )
COMMENTS: SIP MONITOR
ACTIVE 11/73
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05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
State : 50 VERMONT AQCR: 159 CHAMPLAIN VALLEY
County: 007 CHITTENDEN MSA : 0000 NOT IN AN MSA
Site : 0007 CMSA: 0000 DESCRIPTION UNKNOWN
Elevation (MSL) : 342 METERS Date Established : 88/05/01
Land Use :5 FOREST Date Last Updated: 99/01/29
Location Setting : 3 RURAL Date Terminated : / /
City : 00000 NOT IN A CITY
Latitude : 444:31:39:0000 Longitude :-72:52:28:0000
Method of Determ.: Est. of Accuracy :
Datum : Scale :
UTM= Zone: 18 Easting: 668903 Northing : 4932445
Address : PROCTOR MAPLE RESEARCH FARM
Support Agency : 001 VERMONT AGENCY OF ENVIRONMENTAL CONSERVATION
Location Descrip.:
05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
Site-Id : 50-007-0007 State or Local Site Id:
SiteLoc. MSA CMSA
Type Description Rep. Rep.
Tangent Street Type Direction Traffic Flow Street Name
Number Road To Street Flow Year
05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
Site-Id : 50-007-0007
Met-Site-Id.: - - Direction: Type: Distance: 0 METERS
Open Land Direction Max.Beam Min.Beam Receiver Transmitter Beam
Path# Use To Trans. Height Height Height Height Length
( METERS )
COMMENTS: 47-0180-001 -FO1
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05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
State : 50 VERMONT AQCR: 159 CHAMPLAIN VALLEY
County: 007 CHITTENDEN MSA : 1305 BURLINGTON, VT
Site : 0003 CMSA: 0000 DESCRIPTION UNKNOWN
Elevation (MSL) : 64 METERS Date Established : 70/01/01
Land Use :2 COMMERCIAL Date Last Updated: 99/01/29
Location Setting : 1 URBAN AND CE Date Terminated : / /
City : 10675 BURLINGTON
Latitude :+44:28:44:0000 Longitude :-73:12:43:0000
Method of Determ.: Est. of Accuracy :
Datum : Scale :
UTM= Zone: 18 Easting: 642202 Northing: 4926402
Address : ADJ. TO 82 S. WINOOSKI AVENUE
Support Agency : 001 VERMONT AGENCY OF ENVIRONMENTAL CONSERVATION
Location Descrip.:
05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
Site-Id : 50-007-0003 State or Local Site Id:
SiteLoc. MSA CMSA
Type Description Rep. Rep.
Tangent Street Type Direction Traffic Flow Street Name
Number Road To Street Flow Year
1 5 6000
2 5 15000
3 6 6000
05/12/99 AIRS Air Quality Subsystem AMPS 10SB
Browse Site Data
Site-Id : 50-007-0003
Met-Site-Id.: - - Direction: Type: 1 Distance: 0 METERS
Open Land Direction Max.Beam Min.Beam Receiver Transmitter Beam
Path# Use To Trans. Height Height Height Height Length
( METERS )
COMMENTS: VERMONT AGENCY OF ENVIRONMENTAL CONSERVATION
DISCONTINUED
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05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
State : 50 VERMONT AQCR: 159 CHAMPLAIN VALLEY
County: 021 RUTLAND MSA : 0000 NOT IN AN MSA
Site : 0002 CMSA: 0000 DESCRIPTION UNKNOWN
Elevation (MSL) : 165 METERS Date Established : 71/01/01
Land Use :2 COMMERCIAL Date Last Updated: 99/01/29
Location Setting : 1 URBAN AND CE Date Terminated : / /
City : 61225 RUTLAND
Latitude : +43:36:29:0000 Longitude : - 72:58:58:0000
Method of Determ.: Est. of Accuracy :
Datum : Scale :
UTM= Zone: 18 Easting: 662800 Northing : 4830100
Address : PARKING LOT ADJ. TO 9 MERCHANT'S ROW
Support Agency : 001 VERMONT AGENCY OF ENVIRONMENTAL CONSERVATION
Location Descrip.:
05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
Site-Id : 50-021-0002 State or Local Site Id:
SiteLoc. MSA CMSA
Type Description Rep. Rep.
Tangent Street Type Direction Traffic Flow Street Name
Number Road To Street Flow Year
05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
Site-Id: 50-021-0002
Met-Site-Id.: - - Direction: Type: Distance: 0 METERS
Open Land Direction Max.Beam Min.Beam Receiver Transmitter Beam
Path# Use To Trans. Height Height Height Height Length
( METERS )
COMMENTS: LOCATED IN PARKING LOT ADJ TO BUSINESS AND COMMERCIAL
DISTRICT SLAMS SO2
-------
05/12/99 AIRS Air Quality Subsystem AMPS 10SB
Browse Site Data
State : 50 VERMONT AQCR: 221 VERMONT
County: 025 W1NDHAM MSA : 0000 NOT IN AN MSA
Site : 0004 CMSA: 0000 DESCRIPTION UNKNOWN
Elevation (MSL) : • METERS Date Established : 96/03/01
Land Use :2 COMMERCIAL Date Last Updated: 99/01/29
Location Setting : 2 SUBURBAN Date Terminated : / /
City : 07900 BRATTLEBORO
Latitude :+42:53:20:0000 Longitude :-72:33:15:0000
Method of Determ.: MAP Est. of Accuracy : 0.66000SEC
Datum : 27 NAD 27 Scale : 24000C
UTM = Zone : 18 Easting : 699725 Northing : 4751175
Address : 1277 PUTNEY ROAD, RTE 5 BRATTLEBORO
Support Agency : 001 VERMONT AGENCY OF ENVIRONMENTAL CONSERVATION
Location Descrip.:
1277 PUTNEY ROAD, RTE 5 IN AGWAY PARKING LOT
05/12/99 AIRS Air Quality Subsystem AMPS 10SB
Browse Site Data
Site-Id : 50-025-0004 State or Local Site Id:
SiteLoc. MSA CMSA
Type Description Rep. Rep.
5 OTHER
Tangent Street Type Direction Traffic Flow Street Name
Number Road To Street Flow Year
1 5 W 16578 1996 PUTNEY ROAD
05/12/99 AIRS Air Quality Subsystem AMP510SB
Browse Site Data
Site-Id : 50-025-0004
Met-Site-Id.: - - Direction: Type: Distance: 0 METERS
Open Land Direction Max.Beam Min.Beam Receiver Transmitter Beam
Path# Use To Trans. Height Height Height Height Length
( METERS —)
COMMENTS:
-------
APPENDIX B
1998/1999 SUMMARY OF INVALIDATED VOC SAMPLES
-------
Table B-l
Invalid VOC Samples for the 1998/1999 UATMP Season
ERG TD
14780
15367
15435
15437
15467
15509
15672
15695
15697
15707
15759
15756
15778
16133
16316
16695
16869
15826
15828
16611
15502
15540
15542
15705
15727
15729
16359
15326
15405
15602
15604
15217
15686
Comments
Duplicate 1
Duplicate 1
Duplicate 2
2"Hg
0"Hg
NA
Duplicate 1
Duplicate 2
Duplicate 1
Duplicate 2
0"Hg
NA
4"Hg
4"Hg
Site TD
B2LA
BRVT
BUND
BUVT
CANJ
Date Sampled
9/8/98
1/30/99
2/11/99
2/17/99
2/25/99
3/13/99
4/19/99
4/20/99
4/20/99
4/26/99
4/30/99
5/2/99
5/25/99
7/23/99
8/10/99
9/5/99
9/30/99
5/12/99
5/12/99
8/28/99
3/13/99
3/19/99
3/19/99
4/24/99
5/6/99
5/6/99
8/16/99
1/12/99
2/5/99
3/25/99
3/25/99
12/1/98
4/18/99
Invalid Reason
Zero pressure
Carbonyl tube was lost
Zero pressure
Zero pressure
Zero pressure
Zero pressure
Zero pressure
Top of the canister broke
Duplicate was voided
Main breaker was out
Zero pressure
Zero pressure
Zero pressure
Zero pressure
Zero pressure
Zero pressure
Zero pressure
Duplicate was voided
Zero pressure
Pressure too low
Zero pressure
Zero pressure
Zero pressure
Zero pressure
Vacuum too low for analysis
Vacuum too low for analysis
Vacuum too low for analysis
Zero pressure
Improper time setup
Analysis of duplicates didn't
match
Analysis of duplicates didn't
match
Zero pressure
Sample was not received
B-l
-------
Table B-l (Continued)
Invalid VOC Samples for the 1998/1999 UATMP Season
ERO ID
15343
15495
15688
15231
15411
15459
15690
15692
15754
14556
14695
14886
15141
15219
15286
15312
15364
15370
15131
15221
15415
15618
15680
15762
15764
16201
14682
15209
15320
15822
15824
15925
16899
16620
Comments
Duplicate 1
Duplicate 1
Duplicate 2
0"Hg
0"Hg
4"Hg
NA
0"Hg
0"He
Site ID
EPTX
GALA
GREY
HALA
PARR
RUVT
UNVT
Date Sampled
1/6/99
3/7/99
4/18/99
1 1/19/98
2/17/99
2/23/99
4/18/99
4/24/99
5/6/99
9/1/98
9/2/98
9/17/98
10/25/98
11/13/98
12/25/98
1/6/99
1/18/99
1/30/99
10/14/98
12/1/98
2/13/99
3/31/99
4/6/99
5/6/99
5/6/99
7/29/99
9/3/98
1 1/19/98
1/12/99
5/12/99
5/12/99
6/17/99
9/21/99
8/28/99
Invalid Reason
Carbonyl sample not sent
Zero pressure
Sample was not received
Zero pressure
Carbonyl tube was void
Carbonyl tube was void
Carbonyl tube was void
Canister was not sampled
Carbonyl tube was void
Zero pressure
Zero pressure
Zero pressure
No sample taken
No sample taken
Carbonyl tube was void
Zero pressure
Zero pressure
Zero pressure
Zero pressure
Zero pressure
Zero pressure
Zero pressure
Sampler had blown diaphragm
Zero pressure
Duplicate sample voided
Zero pressure
Zero pressure
Zero pressure
Zero pressure
Zero pressure
Duplicate sample voided
Carbonyl tube was void
Canister leaked
Zero pressure
B-2
-------
APPENDIX C
1998/1999 SUMMARY OF INVALIDATED CARBONYL SAMPLES
-------
Table C-l
Invalid Carbonyl Samples for the 1998/1999 UATMP Season
ERO ID
14781
15168
15366
15436
15438
15468
15510
15673
15698
15708
15760/15761
15757/15758
15779/15780
16134
16317
16696
16870
15827
15829
16612
15728
15730
16360
15327
15406
15218
15687
15067
15129
15130
15344
15496
1 568Q
Comments
Duplicate 1
Duplicate 2
Sample & blank
Sample & blank
Sample & blank
Duplicate 1
Duplicate 2
Duplicate 1
Duplicate 2
Duplicate 1
Duplicate 2
Site TD
B2LA
BRVT
BUND
BUVT
CANJ
EPTX
Date
Sampled
9/8/98
1 1/1/98
1/30/99
2/11/99
2/17/99
2/25/99
3/13/99
4/19/99
4/20/99
4/26/99
4/30/99
5/2/99
5/25/99
7/23/99
8/10/99
9/5/99
9/27/99
5/12/99
5/12/99
8/28/99
5/6/99
5/6/99
8/16/99
1/12/99
2/5/99
12/1/98
4/18/99
10/2/98
10/2/98
10/14/98
1/6/99
3/7/99
4/18/99
Invalid Reason
.Canister was void
Canister was void
Carbonyl tube lost
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Main breaker was out
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Improper time setup
Canister was void
Sample was not received
No COC or sampling information
Carbonyl sample not sent
Carbonyl sample not sent
Carbonyl sample not sent
Canister was void
Sample was not received
C-l
-------
Table C-l (Continued)
Invalid Carbonyl Samples for the 1998/1999 UATMP Season
ERG ID
15232
15412
15460
15691
15753
15755
14557/14558
14696
14887/14888
15142
15220
15287
15313
15365
15371
15132
15222
15416
15619
15681
15763
15765
16202
14683
15146
15210
15321
15823
15825
15926
16610
16900
16621
Comments
Duplicate 1
Duplicate 2
Sample & blank
Sample & blank
Duplicate 1
Duplicate 2
Duplicate 1
Duplicate 2
Site TD
GALA
GREY
HALA
PARR
RUVT
IJNVT
Date
Samnled
11/19/98
2/17/99
2/23/99
4/18/99
5/6/99
5/6/99
9/1/98
9/5/98
9/17/98
10/25/98
11/13/98
12/25/98
1/6/99
1/18/99
1/30/99
10/14/98
12/1/98
2/13/99
3/31/99
4/6/99
5/6/99
5/6/99
7/29/99
9/3/98
10/26/98
11/19/98
1/12/99
5/12/99
5/12/99
6/17/99
8/28/99
9/21/99
8/28/99
Invalid Reason
Canister was void
Flow problems
Flow problems
Carbonyl tube was disconnected
Duplicate was voided
Carbonyl sample was not sent
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Canister was void
Carbonyl sample was not sent
Canister was void
Canister was void
Canister was void
Canister was void
Tube was not connected properly
Tube missing from packet
Carbonyl tube was void
Canister was void
C-2
-------
APPENDIX D
1998/1999 SUMMARY TABLES FOR VOC MONITORING
-------
Table D-l
Summary Statistics for VOC Concentrations Measured at Baton Rouge, Louisiana (B2LA)
(Based on 18 Valid Sampling Days)
Compound
Acetylene
yropylene
Dichlorodifluoromethane
Chloromethane
Dichlorotetrafluoroethane
Vinyl Chloride
1, 3 -Butadiene
komomethane
Chloroethane
Acetonitrile
Trichlorofluoromethane
Acrylonitrile
1 , 1 -Dichloroethene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
0
0
14
16
3
16
15
5
0
16
18
Frequency
of
Detections
100%
100%
100%
100%
22%
11%
83%
11%
17%
72%
100%
11%
0%
Range of Measured
Concentrations
Lowest
(ppbv)
0.76
0.55
0.46
0.11
ND
ND
ND
ND
ND
ND
0.20
ND
ND
Highest
(ppbv)
5.34
5.00
0.76
3.11
0.07
0.26
0.44
0.07
0.24
109.00
1.87
1.23
ND
Central Tendency of Measured
Concentrations
Median
(ppbv)
1.59
1.42
0.64
0.90
0.02
0.04
0.09
0.02
0.03
42.87
0.30
0.03
0.02
Arithmetic
Mean
(ppbv)
1.97
1.77
0.63
1.08
0.02
0.05
0.12
0.02
0.05
39.60
0.40
0.11
0.02
Geometric
Mean
(ppbv)
1.70
1.45
0.62
0.85
0.02
0.04
0.08
0.02
0.04
6.78
0.34
0.04
0.02
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
7.23
1.19
0.09
0.79
0.01
0.05
0.11
0.01
0.06
37.56
0.38
0.28
0.00
Coefficient
of
Variation
0.63
0.67
0.14
0.73
0.69
1.10
0.94
0.51
1.09
0.95
0.93
2.61
0.00
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-l
-------
Table D-l (Continued)
Summary Statistics for VOC Concentrations Measured at Baton Rouge, Louisiana (B2LA)
(Based on 18 Valid Sampling Days)
Compound
Methylene Chloride
Trichlorotrifluoroethane
trans- 1 ,2-Dichloroethylene
, 1 -Dichloroethane
Methyl tert-Butyl Ether
Methyl Ethyl Ketone
Chloroprene
cis- 1 ,2-Dichloroethylene
Bromochloromethane
Chloroform
Ethyl tert-Buty] Ether
1 ,2-Dichloroethane
1,1,1-Trichloroethane
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
1
0
18
18
12
0
18
18
18
10
18
16
0
Frequency
of
Detections
94%
100%
0%
0%
33%
100%
0%
0%
0%
44%
0%
11%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
0.08
ND
ND
ND
0.57
ND
ND
ND
ND
ND
ND
0.05
Highest
(ppbv)
0.64
0.59
ND
ND
0.30
7.72
ND
ND
ND
0.37
ND
0.49
0.22
Central Tendency of Measured
Concentrations
Median
(Ppbv)
0.15
0.13
0.03
0.02
0.02
1.11
0.02
0.04
0.02
0.02
0.03
0.04
0.09
Arithmetic
Mean
(ppbv)
0.20
0.19
0.03
0.02
0.07
1.07
0.02
0.04
0.02
0.08
0.03
0.08
0.10
Geometric
Mean
(ppbv)
0.15
0.16
0.03
0.02
0.03
1.01
0.02
0.04
0.02
0.05
0.03
0.05
0.09
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.16
0.14
0.00
0.00
0.10
0.37
0.00
0.00
0.00
0.10
0.00
0.12
0.05
Coefficient
of
Variation
0.82
0.75
0.00
0.00
1.37
0.35
0.00
0.00
0.00
1.23
0.00
1.51
0.51
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-2
-------
Table D-l (Continued)
Summary Statistics for VOC Concentrations Measured at Baton Rouge, Louisiana (B2LA)
(Based on 18 Valid Sampling Days)
Compound
lenzene
Carbon Tetrachloride
tert-Amy\ Methyl Ether
[ ,2-Dichloropropane
ithyl Acrylate
Bromodichloromethane
frichloroethylene
Methyl Methacrylate
ci s- 1 ,3-Dichloropropene
Vlethyl Isobutyl Ketone
trans- 1 ,3-Dichloropropene
^ , 1 ,2-Trichloroethane
Toluene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
18
18
18
18
15
14
18
7
18
18
0
Frequency
of
Detections
100%
100%
0%
0%
0%
0%
17%
22%
0%
61%
0%
0%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
0.44
0.05
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.56
Highest
(ppbv)
1.49
0.17
ND
ND
ND
ND
0.48
0.28
ND
0.33
ND
ND
10.27
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.73
0.10
0.03
0.05
0.02
0.03
0.03
0.03
0.02
0.09
0.02
0.02
1.19
Arithmetic
Mean
(ppbv)
0.77
0.10
0.03
0.05
0.02
0.03
0.06
0.07
0.02
0.12
0.02
0.02
2.02
Geometric
Mean
(ppbv)
0.72
0.09
0.03
0.05
0.02
0.03
0.04
0.05
0.02
0.09
0.02
0.02
1.43
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.31
0.03
0.00
0.00
0.00
0.00
0.11
0.08
0.00
0.09
0.00
0.00
2.37
Coefficient
of
Variation
0.41
0.28
0.00
0.00
0.00
0.00
1.92
1.14
0.00
0.78
0.00
0.00
1.17
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-3
-------
Table D-l (Continued)
Summary Statistics for VOC Concentrations Measured at Baton Rouge, Louisiana (B2LA)
(Based on 18 Valid Sampling Days)
Compound
Dibromochloromethane
1 ,2-Dibromoethane
n-Octane
Tetrachloroethylene
Chlorobenzene
^thylbenzene
n-,p-Xylene
iromoform
Styrene
1 , 1 ,2,2-Tetrachloroethane
9-Xylene
1,3, 5-Trimethylbenzene
1,2, 4-Trimethylbenzene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
18
18
0
7
17
0
0
18
0
17
0
0
0
Frequency
of
Detections
0%
0%
700%
61%
6%
100%
100%
0%
700%
6%
100%
100%
100%
Range of Measured
Concentrations
Lowest
(Ppbv)
ND
ND
0.08
ND
ND
0.12
0.29
ND
0.05
ND
0.15
0.07
0.13
Highest
(Ppbv)
ND
ND
0.83
0.18
0.07
1.83
3.57
ND
7.27
0.03
1.86
2.34
6.85
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.02
0.03
0.74
0.05
0.02
0.26
0.65
0.06
0.20
0.03
0.35
0.12
0.29
Arithmetic
Mean
(Ppbv)
0.02
0.03
0.20
0.06
0.02
0.39
1.03
0.06
0.37
0.03
0.58
0.32
0.85
Geometric
Mean
(ppbv)
0.02
0.03
0.16
0.05
0.02
0.30
0.78
0.06
0.27
0.03
0.43
0.17
0.42
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.00
0.00
0.79
0.04
0.01
0.40
0.89
0.00
0.57
0.00
0.52
0.54
1.57
Coefficient
of
Variation
0.00
0.00
0.93
0.62
0.52
1.02
0.87
0.00
0.99
0.09
0.91
1.69
1.86
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-4
-------
Table D-l (Continued)
Summary Statistics for VOC Concentrations Measured at Baton Rouge, Louisiana (B2LA)
(Based on 18 Valid Sampling Days)
f-~\ 1
Compound
w-Dichlorobenzene
Chloromethylbenzene
»-Dichlorobenzene
p-Dichlorobenzene
1 ,2,4-Trichlorobenzene
Hexachloro- 1 ,3-Butadiene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
18
18
13
18
17
18
Frequency
of
Detections
0%
0%
28%
0%
6%
0%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
ND
ND
ND
ND
ND
Highest
(ppbv)
ND
ND
0.05
ND
0.05
ND
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.05
0.09
0.04
0.05
0.05
0.06
Arithmetic
Mean
(ppbv)
0.05
0.09
0.04
0.05
0.04
0.06
Geometric
Mean
(Ppbv)
0.05
0.09
0.04
0.05
0.04
0.06
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.00
0.00
0.01
0.00
0.01
0.00
Coefficient
of
Variation
0.00
0.00
0.16
0.00
0.13
0.00
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one observation for each
successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central tendency concentrations for these
compounds should adequately represent long-term average concentrations, but the central tendency concentrations of the other compounds (in plain text) may be
influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in italics represent overall site-specific prevalent compounds over
80% for frequency only.
D-5
-------
Table D-2
Summary Statistics for VOC Concentrations Measured at Beulah, North Dakota (BUND)
(Based on 32 Valid Sampling Days)
Compound
Acetylene
yropylene
~)ichlorodifluoromethane
Chloromethane
Dichlorotetrafluoroethane
Vinyl Chloride
1,3-Butadiene
Jromomethane
Chloroethane
Acetonitrile
rrichlorofluoromethane
Acrylonitrile
1 , 1 -Dichloroethene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
0
0
27
31
30
31
29
11
0
30
31
Frequency
of
Detections
100%
100%
100%
100%
16%
3%
6%
3%
9%
66%
100%
6%
3%
Range of Measured
Concentrations
Lowest
(ppbv)
0.29
0.17
0.16
0.52
ND
ND
ND
ND
ND
ND
0.27
ND
ND
Highest
(ppbv)
1.20
1.14
1.06
0.83
0.11
0.11
0.03
0.15
0.29
5.60
0.80
0.15
0.14
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.62
0.33
0.66
0.63
0.02
0.04
0.03
0.02
0.03
0.91
0.35
0.03
0.02
Arithmetic
Mean
(ppbv)
0.62
0.35
0.67
0.62
0.02
. 0.04
0.03
0.02
0.04
1.18
0.40
0.04
0.02
Geometric
Mean
(ppbv)
0.58
0.32
0.65
0.62
0.02
0.04
0.02
0.02
0.04
0.58
0.38
0.03
0.02
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.22
0.17
0.15
0.07
0.02
0.01
0.00
0.02
0.05
1.28
0.73
0.02
0.02
Coefficient
of
Variation
0.35
0.49
0.23
0.10
0.93
0.36
0.05
0.96
1.15
1.09
0.33
0.68
0.89
MR = not reported. Sampling site had contamination problems with Methyl Ethyl Ketone, therefore the whole year of data is not reported for this compound.
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-6
-------
Table D-2 (Continued)
Summary Statistics for VOC Concentrations Measured at Beulah, North Dakota (BUND)
(Based on 32 Valid Sampling Days)
Compound
Methylene Chloride
Trichlorotrifluoroethane
trans- 1 ,2-Dichloroethylene
1 , 1 -Dichloroethane
Methyl te/t-Butyl Ether
Methyl Ethyl Ketone
Chloroprene
cis- 1 ,2-Dichloroethylene
Bromochloromethane
Chloroform
Ethyl tert-Butyl Ether
1 ,2-Dichloroethane
[, 1,1-Trichloroethane
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
32
31
32
NR
32
32
32
31
32
31
0
Frequency
of
Detections
100%
100%
0%
3%
0%
NR
0%
0%
0%
3%
0%
3%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
0.11
0.07
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0.04
Highest
(ppbv)
2.55
0.46
ND
0.09
ND
NR
ND
ND
ND
0.11
ND
0.12
0.18
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.41
0.10
0.03
0.02
0.02
NR
0.02
0.04
0.02
0.02
0.03
0.04
0.06
Arithmetic
Mean
(ppbv)
0.54
0.11
0.03
0.02
0.02
NR
0.02
0.04
0.02
0.02
0.03
0.04
0.07
Geometric
.Mean
(ppbv)
0.44
0.10
0.03
0.02
0.02
NR
0.02
0.04
0.02
0.02
0.03
0.04
0.07
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.49
0.07
0.00
0.01
0.00
NR
0.00
0.00
0.00
0.02
0.00
0.01
0.03
Coefficient
of
Variation
0.91
0.63
0.00
0.76
0.00
NR
0.00
0.00
0.00
0.70
0.00
0.33
0.44
NR = not reported. Sampling site had contamination problems with Methyl Ethyl Ketone, therefore the whole year of data is not reported for this compound.
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-7
-------
Table D-2 (Continued)
Summary Statistics for VOC Concentrations Measured at Beulah, North Dakota (BUND)
(Based on 32 Valid Sampling Days)
Compound
benzene
Carbon Tetrachloride
tert-Amyl Methyl Ether
1 ,2-Dichloropropane
Ethyl Acrylate
Bromodichloromethane
Trichloroethylene
VIethyl Methacrylate
cis- 1 ,3-Dichloropropene
Methyl Isobutyl Ketone
trans- 1 ,3-Dichloropropene
i , 1 ,2-Trichloroethane
Toluene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
1
32
32
32
32
28
32
32
26
32
31
0
Frequency
of
Detections
100%
97%
0%
0%
0%
0%
13%
0%
0%
19%
0%
3%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
0.12
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.14
Highest
(ppbv)
0.56
0.11
ND
ND
ND
ND
0.44
ND
ND
0.61
ND
0.11
1.32
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.23
0.08
0.03
0.05
0.02
0.03
0.03
0.03
0.02
0.04
0.02
0.02
0.31
Arithmetic
Mean
(ppbv)
0.26
0.08
0.03
0.05
0.02
0.03
0.05
0.03
0.02
0.08
0.02
0.02
0.45
Geometric
Mean
(ppbv)
0.24
0.08
0.03
0.05
0.02
0.03
0.03
0.03
0.02
0.05
0.02
0.02
0.36
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.10
0.02
0.00
0.00
0.00
0.00
0.07
0.00
0.00
0.12
0.00
0.02
0.34
Coefficient
of
Variation
0.40
0.21
0.00
0.00
0.00
0.00
1.57
0.00
0.00
1.55
0.00
0.93
0.75
NR = not reported. Sampling site had contamination problems with Methyl Ethyl Ketone, therefore the whole year of data is not reported for this compound.
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-8
-------
Table D-2 (Continued)
Summary Statistics for VOC Concentrations Measured at Beulah, North Dakota (BUND)
(Based on 32 Valid Sampling Days)
Compound
Dibromochloromethane
1 ,2-Dibromoethane
n- Octane
Tetrachloroethylene
Chlorobenzene
Ithylbenzene
m-,p-Xylene
Bromoform
Styrene
. , 1 ,2,2-Tetrachloroethane
o-Xylene
1, 3, 5-Trimethylbenzene
1,2,4- Trimethylbenzene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
32
31
5
25
31
/
0
32
1
31
0
6
0
Frequency
of
Detections
0%
3%
84%
22%
3%
97%
100%
0%
97%
3%
100%
81%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
ND
ND
ND
ND
ND
0.06
ND
ND
ND
0.02
ND
0.04
Highest
(ppbv)
ND
0.08
0.36
0.40
0.10
0.24
0.60
ND
0.75
0.05
0.20
0.11
0.19
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.02
0.03
0.08
0.05
0.02
0.06
0.12
0.06
0. 06
0.03
0. 07
0.04
0.08
Arithmetic
Mean
(ppbv)
0.02
0.03
0. 09
0.06
0.02
0.09
0.17
0.06
0.07
0.03
0.09
0.05
0.09
Geometric
Mean
(ppbv)
0.02
0.03
0.07
0.05
0.02
0.08
0.14
0.06
0.06
0.03
0.08
0.04
0.09
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.00
0.01
0.06
0.06
0.01
0.05
0.12
0.00
0.04
0.00
0.05
0.02
0.04
Coefficient
of
Variation
0.00
0.36
0.77
1.01
0.63
0.57
0.71
0.00
0.59
0.17
0.53
0.38
0.42
NR = not reported. Sampling site had contamination problems with Methyl Ethyl Ketone, therefore the whole year of data is not reported for this compound.
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-9
-------
Table D-2 (Continued)
Summary Statistics for VOC Concentrations Measured at Beulah, North Dakota (BUND)
(Based on 32 Valid Sampling Days)
Compound
n-Dichlorobenzene
Chloromethylbenzene
> -Dichlorobenzene
9-Dichlorobenzene
'. ,2,4-Trichlorobenzene
lexachloro- 1 ,3-Butadiene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
31
32
30
32
30
31
Frequency
of
Detections
3%
0%
6%
0%
6%
3%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
ND
ND
ND
ND
ND
Highest
(ppbv)
0.05
ND
0.05
ND
0.05
0.06
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.05
0.09
0.04
0.05
0.05
0.06
Arithmetic
Mean
(ppbv)
0.05
0.09
0.04
0.05
0.04
0.05
Geometric
Mean
(ppbv)
0.05
0.09
0.04
0.05
0.04
0.05
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.00
0.00
0.00
0.00
0.01
0.00
Coefficient
of
Variation
0.02
0.00
0.10
0.00
0.20
0.08
NR = not reported. Sampling site had contamination problems with Methyl Ethyl Ketone, therefore the whole year of data is not reported for this compound.
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one observation for each
successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central tendency concentrations for these
compounds should adequately represent long-term average concentrations, but the central tendency concentrations of the other compounds (in plain text) may be
influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in italics represent overall site-specific prevalent compounds over
80% for frequency only.
D-10
-------
Table D-3
Summary Statistics for VOC Concentrations Measured at Brattleboro, Vermont (BRVT)
(Based on 31 Valid Sampling Days)
s~~\ 1
Compound
Acetylene
9ropylene
Jichlorodifluoromethane
Chloromethane
Dichlorotetrafluoroethane
Vinyl Chloride
1 ,3-Butadiene
3romomethane
Chloroethane
Acetonitrile
rrichlorofluoromethane
Acrylonitrile
1 , 1 -Dichloroethene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
0
0
27
31
7
31
31
25
0
27
31
Frequency
of
Detections
100%
100%
100%
100%
13%
0%
77%
0%
0%
19%
100%
13%
0%
Range of Measured
Concentrations
Lowest
(ppbv)
0.38
0.36
0.48
0.47
ND
ND
ND
ND
ND
ND
0.24
ND
ND
Highest
(ppbv)
4.20
1.71
1.60
0.92
0.02
ND
0.28
ND
ND
15.25
0.76
0.89
ND
Central Tendency of Measured
Concentrations
Median
(ppbv)
7.27
0.71
0.64
0.63
0.02
0.04
0.07
0.02
0.03
0.11
0.32
0.03
0.02
Arithmetic
Mean
(ppbv)
1.66
0.84
0.67
0.64
0.01
0.04
0.08
0.02
0.03
1.04
0.35
0.08
0.02
Geometric
Mean
(ppbv)
1.39
0.78
0.65
0.64
0.01
0.04
0.07
0.02
0.03
0.20
0.34
0.04
0.02
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
1.09
0.38
0.18
0.10
0.00
0.00
0.07
0.00
0.00
3.06
0.12
0.17
0.00
Coefficient
of
Variation
0.66
0.44
0.27
0.15
0.10
0.00
0.79
0.00
0.00
2.94
0.34
2.09
0.00
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-ll
-------
Table D-3 (Continued)
Summary Statistics for VOC Concentrations Measured at Brattleboro, Vermont (BRVT)
(Based on 31 Valid Sampling Days)
Compound
Vlethylene Chloride
Trichlorotrifluoroethane
trans- 1 ,2-Dichloroethylene
, 1 -Dichloroethane
Methyl tert-Butyl Ether
Methyl Ethyl Ketone
Chloroprene
cis- 1 ,2-Dichloroethylene
Jromochloromethane
Chloroform
Ethyl tert-Butyl Ether
,2-Dichloroethane
1, 1,1-Trichloroethane
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
11
0
31
31
2
1
31
31
31
29
31
31
0
Frequency
of
Detections
65%
100%
0%
0%
94%
97%
0%
0%
0%
6%
0%
0%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
0.05
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.04
Highest
(ppbv)
0.45
0.90
ND
ND
0.78
4.03
ND
ND
ND
0.06
ND
ND
0.10
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.07
0.11
0.03
0.02
0.33
0.59
0.02
0.04
0.02
0.02
0.03
0.04
0.06
Arithmetic
Mean
(ppbv)
0.11
0.14
0.03
0.02
0.36
0.94
0.02
0.04
0.02
0.02
0.03
0.04
0.06
Geometric
Mean
(ppbv)
0.08
0.12
0.03
0.02
0.29
0.66
0.02
0.04
0.02
0.02
0.03
0.04
0.06
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.11
0.15
0.00
0.00
0.19
0.89
0.00
0.00
0.00
0.01
0.00
0.00
0.01
Coefficient
of
Variation
0.97
1.06
0.00
0.00
0.52
0.95
0.00
0.00
0.00
0.31
0.00
0.00
0.19
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-12
-------
Table D-3 (Continued)
Summary Statistics for VOC Concentrations Measured at Brattleboro, Vermont (BRVT)
(Based on 31 Valid Sampling Days)
Compound
Benzene
Carbon Tetrachloride
tert-Amyl Methyl Ether
1 ,2-Dichloropropane
Ethyl Acrylate
iromodichloromethane
frichloroethylene
Methyl Methacrylate
cis- 1 ,3-Dichloropropene
Methyl Isobutyl Ketone
trans- 1,3-Dichloropropene
1 , 1 ,2-Trichloroethane
Toluene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
1
30
31
30
31
28
30
31
22
31
31
0
Frequency
of
Detections
100%
97%
3%
0%
3%
0%
10%
3%
0%
29%
0%
0%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
0.29
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.32
Highest
(ppbv)
1.18
0.12
0.06
ND
0.09
ND
0.09
0.05
ND
0.27
ND
ND
8.69
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.53
0.09
0.03
0.05
0.02
0.03
0.03
0.03 '
0.02
0.04
0.02
0.02
0.93
Arithmetic
Mean
(ppbv)
0.58
0.09
0.03
0.05
0.02
0.03
0.03
0.03
0.02
0.06
0.02
0.02
1.30
Geometric
Mean
(ppbv)
0.54
0.08
0.03
0.05
0.02
0.03
0.03
0.03
0.02
0.05
0.02
0.02
1.02
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.24
0.02
0.01
0.00
0.01
0.00
0.01
0.00
0.00
0.05
0.00
0.00
1.46
Coefficient
of
Variation
0.41
0.23
0.18
0.00
0.56
0.00
0.35
0.12
0.00
0.88
0.00
0.00
1.12
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-13
-------
Table D-3 (Continued)
Summary Statistics for VOC Concentrations Measured at Brattleboro, Vermont (BRVT)
(Based on 31 Valid Sampling Days)
Compound
Dibromochloromethane
1 ,2-Dibromoethane
n-Octane
Tetrachloroethylene
Chlorobenzene
Ithylbenzene
n-,p-Xylene
3romoform
Styrene
1 , 1 ,2,2-Tetrachloroethane
o-Xylene
1,3, 5-Trimethylbenzene
1 , 2,4-Trimethylbenzene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
31
31
5
22
31
0
0
31
1
31
0
1
0
Frequency
of
Detections
0%
0%
84%
29%
0%
100%
100%
0%
97%
0%
100%
97%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
ND
ND
ND
ND
0.09
0.17
ND
ND
ND
0.11
ND
0.10
Highest
(ppbv)
ND
ND
0.14
0.09
ND
0.37
1.07
ND
0.14
ND
0.49
0.13
0.40
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.02 .
0.03
0.07
0.05
0.02
0.16
0.38
0.06
0.07
0.03
0.20 ,
0.07
0.18
Arithmetic
Mean
(ppbv)
0.02
0.03
0.08
0.05
0.02
0.19
0.46
0.06
0.07
0.03
0.24
0.08
0.21
Geometric
Mean
(ppbv)
0.02
0.03
0.07
0.05
0.02
0.18
0.42
0.06
0.07
0.03
0.22
0.08
0.19
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.00
0.00
0.03
0.02
0.00
0.07
0.20
0.00
0.02
0.00
0.10
0.03
0.08
Coefficient
of
Variation
0.00
0.00
0.34
0.31
0.00
0.35
0.45
0.00
0.31
0.00
0.41
0.32
0.37
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-14
-------
Table D-3 (Continued)
Summary Statistics for VOC Concentrations Measured at Brattleboro, Vermont (BRVT)
(Based on 31 Valid Sampling Days)
Compound
n-Dichlorobenzene
Chloromethylben zene
> -Dichlorobenzene
o-Dichlorobenzene
,2,4-Trichlorobenzene
lexachloro- 1 ,3-Butadiene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
30
31
30
30
30
30
Frequency
of
Detections
3%
0%
3%
3%
3%
3%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
ND
ND
ND
ND
ND
Highest
(ppbv)
0.05
ND
0.06
0.06
0.24
0.06
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.05
0.09
0.04
0.05
0.05
0.06
Arithmetic
Mean
(ppbv)
0.05
0.09
0.04
0.05
0.05
0.05
Geometric
Mean
(ppbv)
0.05
0.09
0.04
0.05
0.05
0.05
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.00
0.00
0.00
0.00
0.04
0.00
Coefficient
of
Variation
0.02
0.00
0.09
0.04
0.68
0.02
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one observation for each
successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central tendency concentrations for these
compounds should adequately represent long-term average concentrations, but the central tendency concentrations of the other compounds (in plain text) may be
influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in italics represent overall site-specific prevalent compounds over
80% for frequency only.
D-15
-------
Table D-4
Summary Statistics for VOC Concentrations Measured at Burlington, Vermont (BUVT)
(Based on 31 Valid Sampling Days)
Compound
Acetylene
*ropylene
Dichlorodifluoromethane
Chloromethane
Dichlorotetrafluoroethane
Vinyl Chloride
1, 3 -Butadiene
Bromomethane
Chloroethane
Acetonitrile
Trichlorofluoromethane
Acrylonitrile
1,1-Dichloroethene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
0
0
27
31
7
28
29
26
0
28
30
Frequency
of
Detections
100%
100%
100%
100%
13%
0%
97%
10%
6%
16%
100%
10%
3%
Range of Measured
Concentrations
Lowest
(ppbv)
0.58
0.80
0.53
0.44
ND
ND
ND
ND
ND
ND
0.24
ND
ND
Highest
(ppbv)
5.16
1.98
0.90
0.85
0.02
ND
0.29
0.17
0.06
17.34
0.90
0.27
0.10
Central Tendency of Measured
Concentrations
Median
(ppbv)
2.15
1.20
0.65
0.64
0.02
0.04
0.14
0.02
0.03
0.11
0.34
0.03
0.02
Arithmetic
Mean
(ppbv)
2.38
1.22
0.67
0.64
0.01
0.04
0.15
0.03
0.03
0.89
0.37
0.05
0.02
Geometric
Mean
(ppbv)
2.77
1.19
0.66
0.63
0.01
0.04
0.14
0.02
0.03
0.17
0.36
0.04
0.02
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
1.02
0.30
0.09
0.09
0.00
0.00
0.06
0.03
0.01
3.19
0.13
0.06
0.01
Coefficient
of
Variation
0.43
0.24
0.14
0.14
0.12
0.00
0.36
1.06
0.17
3.57
0.35
1.24
0.64
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-16
-------
Table D-4 (Continued)
Summary Statistics for VOC Concentrations Measured at Burlington, Vermont (BUVT)
(Based on 31 Valid Sampling Days)
Compound
Methylene Chloride
Trichlorotrifluoroethane
trans- 1 ,2-Dichloroethylene
1 , 1 -Dichloroethane
Methyl tert-Butyl Ether
Methyl Ethyl Ketone
Chloroprene
ci s- 1 ,2-Dichloroethylene
Bromochloromethane
Chloroform
ithyl tert-Butyl Ether
,2-Dichloroethane
j 1,1-Trichloroethane
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
3
1
31
31
1
0
31
30
31
26
31
31
0
Frequency
of
Detections
90%
97%
0%
0%
97%
100%
0%
3%
0%
16%
0%
0%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
ND
ND
ND
ND
0.09
ND
ND
ND
ND
ND
ND
0.05
Highest
(ppbv)
1.68
0.14
ND
ND
0.80
3.71
ND
0.05
ND
0.04
ND
ND
0.08
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.11
0.09
0.03
0.02
0.37
0.46
0.02
0.04
0.02
0.02
0.03
0.04
0.06
Arithmetic
Mean
(ppbv)
0.21
0.09
0.03
0.02
0.36
0.66
0.02
0.04
0.02
, 0.02
• 0.03
0.04
• 0.06
Geometric
Mean
(ppbv)
0.13
0.08
0.03
0.02
0.30
0.49
0.02
0.04
0.02
0.02
0.03
0.04
0.06
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.31
0.02
0.00
0.00
0.17
0.74
0.00
0.00
0.00
0.01
0.00
0.00
0.01
Coefficient
of
Variation
1.49
0.24
0.00
0.00
0.48
1.13
0.00
0.08
0.00
0.27
0.00
0.00
0.15
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-17
-------
Table D-4 (Continued)
Summary Statistics for VOC Concentrations Measured at Burlington, Vermont (BUVT)
(Based on 31 Valid Sampling Days)
Compound
Benzene
Carbon Tetrachloride
tert-Amyl Methyl Ether
; ,2-Dichloropropane
ithyl Aery late
Bromodichloromethane
frichloroethylene
VIethyl Methacrylate
cis- 1 ,3-Dichloropropene
Methyl Isobutyl Ketone
trans- 1 ,3-Dichloropropene
, 1 ,2-Trichloroethane
Toluene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
1
31
31
31
31
30
31
31
27
31
31
0
Frequency
of
Detections
100%
97%
0%
0%
0%
0%
3%
0%
0%
13%
0%
0%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
0.51
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.96
Highest
(ppbv)
1.33
0.12
ND
ND
ND
ND
0.03
ND
ND
0.26
ND
ND
4.23
Central Tendency of Measured
Concentrations
Median
(Ppbv)
0.81
0.09
0.03
0.05
0.02
0.03
0.03
0.03
0.02
0.04
0.02
0.02
1.68
Arithmetic
Mean
(ppbv)
0.86
0.09
0.03
0.05
0.02
0.03
0.03
0.03
0.02
0.05
0.02
0.02
1.85
Geometric
Mean
(Ppbv)
0.84
0.09
0.03
0.05
0.02
0.03
0.03
0.03
0.02
0.04
0.02
0.02
7.75
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.23
0.02
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.04
0.00
0.00
0.67
Coefficient
of
Variation
0.26
0.19
0.00
0.00
0.00
0.00
0.04
0.00
0.00
0.91
0.00
0.00
0.37
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-18
-------
Table D-4 (Continued)
Summary Statistics for VOC Concentrations Measured at Burlington, Vermont (BUVT)
(Based on 31 Valid Sampling Days)
Compound
)ibromochloromethane
1 ,2-Dibromoethane
n-Octane
Tetrachloroethylene
Chlorobenzene
Ethylbenzene
m-,p-Xylene
Bromoform
Styrene
1 , 1 ,2,2-Tetrachloroethane
o-Xylene
1, 3, 5-Trimethylbenzene
1,2,4-Trimethylbenzene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
31
31
0
21
31
0
0
31
1
31
0
1
0
Frequency
of
Detections
0%
0%
100%
32%
0%
100%
100%
0%
97%
0%
100%
97%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
ND
0.03
ND
ND
0.21
0.50
ND
ND
ND
0.28
ND
0.18
Highest
(ppbv)
ND
ND
0.36
0.07
ND
0.52
1.34
ND
0.23
ND
0.67
0.19
0.59
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.02
0.03
0.09
0.05
0.02
0.28
0.77
0.06
0.09
0.03
0.39
0.12
0.32
Arithmetic
Mean
(ppbv)
0.02
0.03
0.10
0.04
0.02
0.31
0.84
0.06
0.09
0.03
0.42
0.12
0.34
Geometric
Mean
(ppbv)
0.02
0.03
0.09
0.04
0.02
0.30
0.81
0.06
0.09
0.03
0.40
0.12
0.33
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.00
0.00
0.06
0.01
0.00
0.08
0.22
0.00
0.04
0.00
0.11
0.03
0.10
Coefficient
of
Variation
0.00
0.00
0.59
0.31
0.00
0.26
0.26
0.00
0.39
0.00
0.26
0.27
0.29
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-19
-------
Table D-4 (Continued)
Summary Statistics for VOC Concentrations Measured at Burlington, Vermont (BUVT)
(Based on 31 Valid Sampling Days)
t~* J
Compound
n-Dichlorobenzene
Chloromethylbenzene
>-Dichlorobenzene
9-Dichlorobenzene
i ,2,4-Trichlorobenzene
Hexachloro- 1 ,3-Butadiene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
31
31
30
31
30
30
Frequency
of
Detections
0%
0%
3%
0%
3%
3%
Range of Measured
Concentrations
Lowest
(Ppbv)
ND
ND
ND
ND
ND
ND
Highest
(ppbv)
ND
ND
0.04
ND
0.05
0.06
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.05
0.09
0.04
0.05
0.05
0.06
Arithmetic
Mean
(ppbv)
0.05
0.09
0.04
0.05
0.04
0.05
Geometric
Mean
(ppbv)
0.05
0.09
0.04
0.05
0.04
0.05
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.00
0.00
0.00
0.00
0.00
0.00
Coefficient
of
Variation
0.00
0.00
0.09
0.00
0.03
0.03
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one observation for each
successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central tendency concentrations for these
compounds should adequately represent long-term average concentrations, but the central tendency concentrations of the other compounds (in plain text) may be
influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in italics represent overall site-specific prevalent compounds over
80% for frequency only.
D-20
-------
Table D-5
Summary Statistics for VOC Concentrations Measured at Camden, New Jersey (CANJ)
(Based on 29 Valid Sampling Days)
Compound
Acetylene
yropylene
Dichlorodifluoromethane
Chloromethane
Dichlorotetrafl uoroeth ane
Vinyl Chloride
i ,3-Butadiene
Bromomethane
Chloroethane
Acetonitrile
rrichlorofluoromethane
Acrylonitrile
, 1 -Dichloroethene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
0
0
25
28
7
20
26
23
0
17
28
Frequency
of
Detections
100%
100%
100%
100%
17%
7%
77%
33%
13%
23%
100%
43%
7%
Range of Measured
Concentrations
Lowest
(ppbv)
0.63
0.25
0.23
0.24
ND
ND
ND
ND
ND
ND
0.13
ND
ND
Highest
(ppbv)
3.76
6.23
0.91
1.21
0.02
0.04
0.32
0.18
0.11
2.65
0.59
1.15
0.02
i
Central Tendency of Measured
( Concentrations
i
Median
(ppbv)
1.50
0.94
0.66
0.74
0.02 1
0.04
0.04
0.02 '
0.03
0.11
0.32
0.03
0.02'
Arithmetic
Mean
(ppbv)
7.75
7.22
0.66
0.77
0.01
0.03
0.07
0.04
0.03
0.35
0.33
0.37
0.02
Geometric
Mean
(ppbv)
1.56
0.95
0.64
0.73
0.01
0.03
0.05
0.03
0.03
0.16
0.32
0.11
0.02
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.89
1.11
0.13
0.23
0.00
0.00
0.06
0.04
0.02
0.65
0.09
0.45
0.00
Coefficient
of
Variation
0.57
0.91
0.20
0.30
0.16
0.13
0.92
1.13
0.48
1.85
0.28
1.21
0.13
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-21
-------
Table D-5 (Continued)
Summary Statistics for VOC Concentrations Measured at Camden, New Jersey (CANJ)
(Based on 29 Valid Sampling Days)
Compound
Methylene Chloride
Trichlorotrifluoroethane
trans- 1 ,2-Dichloroethylene
1,1-Dichloroethane
Methyl tert-Butyl Ether
Methyl Ethyl Ketone
Chloroprene
cis- 1 ,2-Dichloroethylene
Jromochloromethane
Chloroform
Ethyl tert-Butyl Ether
i ,2-Dichloroethane
1,1,1- Trichloroethane
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
/
0
28
28
0
0
28
28
28
27
28
28
0
Frequency
of
Detections
97%
100%
7%
7%
100%
100%
1%
1%
7%
10%
7%
7%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
0.03
ND
ND
0.24
0.06
ND
ND
ND
ND
ND
ND
0.02
Highest
(ppbv)
0.43
0.14
0.03
0.02
2.22
1.87
0.02
0.04
0.02
0.02
0.03
0.04
0.17
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.13
0.09
0.03
0.02
0.83
0.62
0.02
0.04
0.02
0.02
0.03
0.04
0. 07
Arithmetic
Mean
(ppbv)
0.16
0.09
0.02
0.01
0.92
0.73
0.01
0.03
0.02
0.02
0.02
0.04
0.07
Geometric
Mean
(ppbv)
0.14
0.09
0.02
0.01
0.78
0.61
0.01
0.03
0.02
0.02
0.02
0.04
0.07
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.10
0.02
0.00
0.00
0.50
0.40
0.00
0.00
0.00
0.00
0.00
0.01
0.03
Coefficient
of
Variation
0.59
0.24
0.13
0.13
0.54
0.55
0.13
0.13
0.13
0.16
0.13
0.13
0.37
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-22
-------
Table D-5 (Continued)
Summary Statistics for VOC Concentrations Measured at Camden, New Jersey (CANJ)
(Based on 29 Valid Sampling Days)
Compound
Benzene
Carbon Tetrachloride
tert-Amyl Methyl Ether
,2-Dichloropropane
Ethyl Acrylate
Jromodichloromethane
rrichloroethylene
Methyl Methacrylate
cis- 1 ,3-Dichloropropene
VIethyl Isobutyl Ketone
trans- 1 ,3-Dichloropropene
, 1 ,2-Trichloroethane
^oluene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
27
28
28
28
24
28
28
22
28
28
0
Frequency
of
Detections
100%
100%
10%
7%
7%
7%
20%
7%
7%
27%
7%
7%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
0.20
0.03
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.35
Highest
(ppbv)
LOO
0.11
0.03
0.05
0.02
0.03
0.07
0.03
0.02
0.18
0.02
0.02
1.94
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.59
0.09
0.03
0.05
0.02
0.03
0.03
0.03
0.02
0.04
0.02
0.02
1.11
Arithmetic
Mean
(ppbv)
0.58
0.09
0.03
0.04
0.02
0.02
0.03
0.03
0.01
0.05
0.01
0.01
1.08
Geometric
Mean
(ppbv)
0.54
0.08
0.03
0.04
0.02
0.02
0.03
0.03
0.01
0.04
0.01
0.01
0.98
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.21
0.02
0.00
0.01
0.00
0.00
0.01
0.00
0.00
0.03
0.00
0.00
0.44
Coefficient
of
Variation
0.36
0.25
0.14
0.13
0.13
0.13
0.36
0.13
0.13
0.70
0.13
0.13
0.41
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-23
-------
Table D-5 (Continued)
Summary Statistics for VOC Concentrations Measured at Camden, New Jersey (CANJ)
(Based on 29 Valid Sampling Days) >
Compound
Dibromochloromethane
[ ,2-Dibromoethane
i-Octane
Tetrachloroethylene
Chlorobenzene
Ethylbenzene
n-,p-Xylene
Bromoform
Styrene
1 , 1 ,2,2-Tetrachloroethane
9-Xylene
1, 3, 5-Trimethylbenzene
1,2,4- Trimethylbeniene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
28
28
1
1
28
0
0
28
1
28
0
2
0
Frequency
of
Detections
7%
7%
97%
77%
7%
100%
100%
7%
97%
7%
100%
93%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
ND
ND
ND
ND
0.05
0.13
ND
ND
ND
0.06
ND
0.05
Highest
(ppbv)
0.02
0.03
0.36
0.15
0.02
0.26
0.76
0.06
0.79
0.03
0.37
0.13
0.38
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.02
0.03
0.09
0.05
0.02
0.18
0.47
0.06
0.07
0.03
0.23
0.08
0.20
Arithmetic
Mean
(ppbv)
0.02
0.02
0.10
0.07
0.02
0.17
0.44
0.06
0.08
0.02
0.22
0.08
0.20
Geometric
Mean
(ppbv)
0.02
0.02
0.09
0.06
0.02
0.16
0.40
0.06
0.07
0.02
0.21
0.07
0.18
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.00
0.00
0.06
0.03
0.00
0.06
0.17
0.01
0.04
0.00
0.08
0.02
0.08
Coefficient
of
Variation
0.13
0.13
0.58
0.50
0.13
0.34
0.38
0.13
0.47
0.13
0.36
0.31
0.38
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-24
-------
Table D-5 (Continued)
Summary Statistics for VOC Concentrations Measured at Camden, New Jersey (CANJ)
(Based on 29 Valid Sampling Days)
Compound
w-Dichlorobenzene
Chloromethylbenzene
i -Dichlorobenzene
o-Dichlorobenzene
1 ,2,4-Trichlorobenzene
Hexachloro- 1 ,3-Butadiene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
28
28
12
28
27
28
Frequency
of
Detections
7%
7%
60%
7%
10%
7%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
ND
ND
ND
ND
ND
Highest
(Ppbv)
0.05
0.09
0.11
0.05
0.05
0.06
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.05
0.09
0.04
0.05
0.05
0.06
Arithmetic
Mean
(ppbv)
0.04
0.09
0.05
0.05
0.04
0.05
Geometric
Mean
(ppbv)
0.04
0.09
0.05
0.05
0.04
0.05
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.01
0.01
0.02
0.01
0.01
0.01
Coefficient
of
Variation
0.13
0.13
0.46
0.13
0.20
0.13
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one observation for each
successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central tendency concentrations for these
compounds should adequately represent long-term average concentrations, but the central tendency concentrations of the other compounds (in plain text) may be
influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in italics represent overall site-specific prevalent compounds over
80% for frequency only.
D-25
-------
Table D-6
Summary Statistics for VOC Concentrations Measured at El Paso, Texas (EPTX)
(Based on 32 Valid Sampling Days)
Compound
Acetylene
9ropylene
Jichlorodifluoromethane
Chloromethane
Dichlorotetrafluoroethane
Vinyl Chloride
1,3 -Butadiene
iromomethane
Chloroethane
Acetonitrile
Trichlorofluoromethane
Acrylonitrile
j 1 -Dichloroethene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
0
0
23
27
7
25
28
22
0
17
28
Frequency
of
Detections
100%
100%
100%
100%
28%
16%
97%
22%
13%
31%
100%
47%
13%
Range of Measured
Concentrations
Lowest
(ppbv)
1.45
0.35
0.15
0.20
ND
ND
ND
ND
ND
ND
0.07
ND
ND
Highest
(ppbv)
18.89
5.41
1.67
1.14
0.02
0.09
0.79
0.10
0.03
43.48
1.20
1.64
0.02
Central Tendency of Measured
Concentrations
Median
(ppbv) •
3.89
1.35
0.68
0.85
0.02
0.04
0.77
0.02
0.03
0.11
0.31
0.03
0.02
Arithmetic
Mean
(ppbv)
5.14
1.77
0.69
0.81
0.01
0.03
0.24
0.02
0.03
2.36
0.34
0.36
0.02
Geometric
Mean
(ppbv)
4.31
1.48
0.64
0.76
0.01
0.03
0.79
0.02
0.03
0.20
0.30
0.11
0.02
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
3.54
1.18
0.25
0.23
0.00
0.01
0.75
0.02
0.01
7.99
0.19
0.45
0.00
Coefficient
of
Variation
0.69
0.67
0.37
0.28
0.25
0.35
0.72
0.74
0.21
3.38
0.55
1.27
0.21
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-26
-------
Table D-6 (Continued)
Summary Statistics for VOC Concentrations Measured at El Paso, Texas (EPTX)
(Based on 32 Valid Sampling Days)
Compound
\lethylene Chloride
Trichlorotrifluoroethane
trans- 1 ,2-Dichloroethylene
1,1-Dichloroethane
Methyl tert -Butyl Ether
Methyl Ethyl Ketone
Chloroprene
cis- \ ,2-Dichloroethylene
komochloromethane
Chloroform
Ethyl tert-Butyl Ether
1 ,2-Dichloroethane
1,1,1- Trichloroethane
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
28
28
8
0
28
28
28
28
28
28
1
Frequency
of
Detections
100%
100%
13%
13%
75%
100%
13%
13%
13%
13%
13%
13%
97%
Range of Measured
Concentrations
Lowest
(ppbv)
0.23
0.02
ND
ND
ND
0.18
ND
ND
ND
ND
ND
ND
ND
Highest
(ppbv)
3.45
0.13
0.03
0.02
1.69
3.39
0.02
0.04
0.02
0.02
0.03
0.04
0.16
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.71
0.10
0.03
0.02
0.24
0.79
0.02
0.04
0.02
0.02
0.03
0.04
0.06
Arithmetic
Mean
(ppbv)
0.83
0.09
0.02
0.01
0.39
0.98
0.01
0.03
0.02
0.02
0.02
0.04
0.06
Geometric
Mean
(ppbv)
0.70
0.09
0.02
0.01
0.15
0.84
0.01
0.03
0.02
0.02
0.02
0.04
0.06
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.58
0.02
0.00
0.00
0.43
0.62
0.00
0.01
0.00
0.00
0.00
0.01
0.03
Coefficient
of
Variation
0.70
0.27
0.21
0.21
1.10
0.63
0.21
0.21
0.21
0.21
0.21
0.21
0.42
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-27
-------
Table D-6 (Continued)
Summary Statistics for VOC Concentrations Measured at El Paso, Texas (EPTX)
(Based on 32 Valid Sampling Days)
Compound
benzene
Carbon Tetrachloride
tert-Amyl Methyl Ether
1 ,2-Dichloropropane
Ethyl Acrylate
komodichloromethane
Prichloroethylene
VIethyl Methacrylate
cis- 1 ,3-Dichloropropene
Methyl Isobutyl Ketone
trans-\ ,3-Dichloropropene
1 , 1 ,2-Trichloroethane
toluene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
11
28
28
28
24
28
28
23
28
28
0
Frequency
of
Detections
100%
100%
66%
13%
13%
13%
25%
13%
13%
28%
13%
13%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
0.47
0.01
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.46
Highest
(ppbv)
3.36
0.11
1.05
0.05
0.19
0.03
0.11
0.03
0.02
0.27
0.02
0.02
7.33
Central Tendency of Measured
Concentrations
Median
(ppbv)
1.24
0.08
0.10
0.05
0.02
0.03
0.03
0.03
0.02
0.04
0.02
0.02
2.47
Arithmetic
Mean
(ppbv)
7.35
0.08
0.28
0.04
0.02
0.02
0.03
0.03
0.01
0.05
0.01
0.01
2.93
Geometric
Mean
(ppbv)
1.20
0.07
0.12
0.04
0.02
0.02
0.03
0.03
0.01
0.04
0.01
0.01
2.43
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.69
0.02
0.32
0.01
0.03
0.00
0.02
0.01
0.00
0.05
0.00
0.00
1.74
Coefficient
of
Variation
0.51
0.32
1.13
0.21
1.25
0.21
0.71
0.21
0.21
0.92
0.21
0.21
0.60
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-28
-------
Table D-6 (Continued)
Summary Statistics for VOC Concentrations Measured at El Paso, Texas (EPTX)
(Based on 32 Valid Sampling Days)
Compound
Dibromochloromethane
1 ,2-Dibromoethane
i- Octane
Tetrachloroethylene
Chlorobenzene
Ithylbenzene
n-,p-Xylene
Bromoform
Styrene
1 , 1 ,2,2-Tetrachloroethane
9-Xylene
1, 3, 5-Trimethylbenzene
1,2,4-Trimethylbenzene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
28
28
0
16
28
0
0
28
0
28
0
0
0
Frequency
of
Detections
13%
13%
700%
50%
13%
100%
100%
13%
100%
13%
100%
100%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
ND
0.03
ND
ND
0.12
0.36
ND
0.02
ND
0.16
0.04
0.08
Highest
(ppbv)
0.02
0.03
0.31
0.14
0.02
28.28
98.76
0.06
1.81
0.03
44.77
0.43
1.27
Central Tendency of Measured
Concentrations
i
Median
(ppbv)
0.02
0.03
0.72
0.05
0.02
0.43
1.16
0.06
0.77
0.03
0.55
0.17
0.47
Arithmetic
Mean
(ppbv)
0.02
0.02
0.14
0.05
0.02
1.33
4.28
0.06
0.79
0.02
1.97
0.18
0.51
Geometric
Mean
(ppbv)
0.02
0.02
0.72
0.04
0.02
0.46
1.23
0.05
0.72
0.02
0.59
0.15
0.42
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.00
0.00
0.05
0.02
0.00
4.92
17.25
0.01
0.31
0.00
7.82
0.10
0.30
Coefficient
of
Variation
0.21
0.21
0.53
0.52
0.21
3.71
4.03
0.21
1.64
0.21
3.97
0.54
0.59
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-29
-------
Table D-6 (Continued)
Summary Statistics for VOC Concentrations Measured at El Paso, Texas (EPTX)
(Based on 32 Valid Sampling Days)
Compound
n-Dichlorobenzene
Chloromethylbenzene
r-Dichlorobenzene
9-Dichlorobenzene
1 ,2,4-Trichlorobenzene
Hexachloro- 1 ,3-Butadiene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
27
28
8
28
26
27
Frequency
of
Detections
16%
13%
75%
13%
19%
16%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
ND
ND
ND
ND
ND
Highest
(ppbv)
0.13
0.09
0.15
0.05
0.06
0.06
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.05
0.09
0.04
0.05
0.05
0.06
Arithmetic
Mean
(ppbv)
0.04
0.08
0.05
0.05
0.04
0.05
Geometric
Mean
(ppbv)
0.04
0.08
0.04
0.04
0.04
0.05
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.02
0.02
0.03
0.01
0.01
0.01
Coefficient
of
Variation
0.41
0.21
0.69
0.21
0.21
0.20
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one observation for each
successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central tendency concentrations for these
compounds should adequately represent long-term average concentrations, but the central tendency concentrations of the other compounds (in plain text) may be
influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in italics represent overall site-specific prevalent compounds over
80% for frequency only.
D-30
-------
Table D-7
Summary Statistics for VOC Concentrations Measured at Garyville, Louisiana (GALA)
(Based on 28 Valid Sampling Days)
Compound
Acetylene
^ropylene
Jichlorodifluoromethane
Chloromethane
Dichlorotetrafluoroethane
Vinyl Chloride
1,3-Butadiene
Bromomethane
Chloroethane
Acetonitrile
rrichlorofluoromethane
Acrylonitrile
, 1-Dichloroethene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
1
0
0
1
24
25
12
24
26
19
0
25
25
Frequency
of
Detections
96%
100%
100%
96%
14%
11%
57%
14%
7%
32%
100%
11%
11%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
0.01
0.01
ND
ND
ND
ND
ND
ND
ND
0.01
ND
ND
Highest
(ppbv)
3.89
22.73
1.64
2.59
0.02
0.14
0.52
0.18
0.03
24.67
1.10
0.11
0.05
Central Tendency of Measured
• Concentrations
Median
(ppbv)
1.08
0.71
0.67
1.06
0.02
0.04
0.03
0.02
0.03
0.11
0.31
0.03
0.02
Arithmetic
Mean
(ppbv)
1.29
1.79
0.71
1.10
0.01
0.04
0.10
0.03
0.03
1.72
0.37
0.03
0.02
Geometric
Mean
(ppbv)
1.01
0.78
0.60
0.83
0.01
0.03
0.05
0.02
0.03
0.23
0.30
0.03
0.02
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.85
4.22
0.27
0.55
0.00
0.02
0.13
0.03
0.00
4.87
0.22
0.02
0.01
Coefficient
of
Variation
0.66
2.36
0.38
0.50
0.17
0.57
1.31
1.21
0.16
2.84
0.60
0.53
0.33
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-31
-------
Table D-7 (Continued)
Summary Statistics for VOC Concentrations Measured at Garyville, Louisiana (GALA)
(Based on 28 Valid Sampling Days)
Compound
\lethylene Chloride
Trichlorotrifluoroethane
trans- 1 ,2-Dichloroethylene
1 , 1 -Dichloroethane
Methyl tert-Butyl Ether
Methyl Ethyl Ketone
Chloroprene
cis- 1 ,2-Dichloroethylene
Bromochloromethane
Chloroform
Ethyl tert-Buty] Ether
,2-Dichloroethane
Z, 1,1-Trichloroethane
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
3
0
26
26
21
0
19
26
26
22
26
25
0
Frequency
of
Detections
89%
100%
7%
7%
25%
100%
32%
7%
7%
21%
7%
11%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
0.01
ND
ND
ND
0.01
ND
ND
ND
ND
ND
ND
0.02
Highest
(Ppbv)
3.09
0.21
0.03
0.02
0.41
1.66
2.59
0.04
0.02
0.06
0.03
0.30
26.92
Central Tendency of Measured
Concentrations
Median1
(ppbv)
0.09
0.11
0.03
0.02
0.02
0.70
0.02
0.04
0.02
0.02
0.03
0.04
0.14
Arithmetic
Mean
(ppbv)
0.33
0.11
0.02
0.01
0.04
0.69
0.27
0.03
0.02
0.02
0.02
0.05
1.21
Geometric
Mean
(ppbv)
0.12
0.10
0.02
0.01
0.02
0.56
0.04
0.03
0.02
0.02
0.02
0.04
0.18
Variability in
Measured
Concentrations
Standard
Deviation
(Ppbv)
0.70
0.04
0.00
0.00
0.08
0.34
0.60
0.01
0.00
0.01
0.00
0.05
5.05
Coefficient
of
Variation
2.09
0.39
0.16
0.16
2.02
0.49
2.25
0.16
0.16
0.47
0.16
1.05
4.16
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-32
-------
Table D-7 (Continued) ,
Summary Statistics for VOC Concentrations Measured at Garyville, Louisiana (GALA)
(Based on 28 Valid Sampling Days)
Compound
benzene
Carbon Tetrachloride
tert-Amy\ Methyl Ether
1 ,2-Dichloropropane
Ethyl Acrylate
Bromodichloromethane
Trichloroethylene
Methyl Methacrylate
cis- 1 ,3-Dichloropropene
Methyl Isobutyl Ketone
trans- 1 ,3-Dichloropropene
, 1 ,2-Trichloroethane
Toluene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
25
26
26
26
21
26
26
21
26
26
0
Frequency
of
Detections
100%
100%
11%
7%
7%
7%
25%
7%
7%
25%
7%
7%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
0.02
0.02
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.03
Highest
(ppbv)
1.13
0.12
0.37
0.05
0.02
0.03
0.08
0.03
0.02
0.09
0.02
0.02
72.75
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.42
0.09
0.03
0.05
0.02
0.03
0.03
0.03
0.02
0.04
0.02
0.02
0.85
Arithmetic
Mean
(ppbv)
0.48
0.09
0.04
0.04
0.02
0.02
0.03
0.03
0.01
0.04
0.01
0.01
1.39
Geometric
Mean
(ppbv)
0.40
0.08
0.03
0.04
0.02
0.02
0.03
0.03
0.01
0.04
0.01
0.01
0.81
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.25
0.02
0.07
0.01
0.00
0.00
0.01
0.00
0.00
0.02
0.00
0.00
2.33
Coefficient
of
Variation
0.52
0.27
1.59
0.16
0.16
0.16
0.39
0.16
0.16
0.45
0.16
0.16
1.68
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
-------
Table D-7 (Continued)
Summary Statistics for VOC Concentrations Measured at Garyville, Louisiana (GALA)
(Based on 28 Valid Sampling Days)
Compound
Dibromochloromethane
1 ,2-Dibromoethane
n-Octane
Petrachloroethylene
Chlorobenzene
Vthylbenzene
n-,p-Xylene
Bromoform
Styrene
, 1 ,2,2-Tetrachloroethane
9-Xylene
1,3,5- Trimethylbenzene
1 ,2,4-Trimethylbenzene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
26
26
;
14
26
0
0
26
2
26
0
3
0
Frequency
of
Detections
7%
7%
96%
50%
7%
100%
100%
7%
93%
7%
100%
89%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
ND
ND
ND
ND
0.03
0.02
ND
ND
ND
0.01
ND
0.02
Highest
(ppbv)
0.02
0.03
0.56
2.38
0.02
0.59
1.58
0.06
0.33
0.03
0.79
0.23
0.65
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.02
0.03
0.08
0.05
0.02
0.15
0.34
0.06
0.07
0.03
0.19
0.06
0.15
Arithmetic
Mean
(ppbv)
0.02
0.02
0.12
0.29
0.02
0.18
0.42
0.06
0.08
0.02
0.22
0.07
0.18
Geometric
Mean
(ppbv)
0.02
0.02
0.09
0.11
0.02
0.15
0.33
0.06
0.07
0.02
0.17
0.06
0.15
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.00
0.00
0.72
0.52
0.00
0.11
0.31
0.01
0.06
0.00
0.15
0.04
0.12
Coefficient
of
Variation
0.16
0.16
1.03
1.78
0.16
0.63
0.73
0.16
0.72
0.16
0.69
0.58
0.66
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate ju>i'. --ne
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-34
-------
Table D-7 (Continued)
Summary Statistics for VOC Concentrations Measured at Garyville, Louisiana (GALA)
(Based on 28 Valid Sampling Days)
Compound
n-Dichlorobenzene
Chloromethylbenzene
>-Dichlorobenzene
o-Dichlorobenzene
! ,2,4-Trichlorobenzene
Hexachloro- 1 ,3 -Butadiene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
26
26
23
25
24
26
Frequency
of
Detections
7%
7%
18%
11%
14%
7%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
ND
ND
ND
ND
ND
Highest
(ppbv)
0.05
0.09
0.04
0.05
0.05
0.06
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.05
0.09
0.04
0.05
0.05
0.06
Arithmetic
Mean
(ppbv)
0.04
0.09
0.04
0.05
0.04
0.05
Geometric
Mean
(ppbv)
0.04
0.08
0.04
0.05
0.04
0.05
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.01
0.01
0.01
0.01
0.01
0.01
Coefficient
of
Variation
0.16
0.16
0.20
0.16
0.22
0.16
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one observation for each
successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central tendency concentrations for these
compounds should adequately represent long-term average concentrations, but the central tendency concentrations of the other compounds (in plain text) may be
influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in italics represent overall site-specific prevalent compounds over
80% for frequency only.
D-35
-------
Table D-8
Summary Statistics for VOC Concentrations Measured at Hahnville, Louisiana (HALA)
(Based on 25 Valid Sampling Days)
Compound
Acetylene
9ropylene
Jichlorodifluoromethane
Chloromethane
Dichlorotetrafluoroethane
Vinyl Chloride
1 ,3-Butadiene
Bromome thane
Chloroethane
Acetonitrile
Trichlorofluoromethane
Acrylonitrile
i , 1 -Dichloroethene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
0
0
23
25
7
24
24
16
0
18
25
Frequency
of
Detections
100%
100%
100%
100%
8%
0%
72%
4%
4%
36%
100%
28%
0%
Range of Measured
Concentrations
Lowest
(ppbv)
0.44
0.62
0.55
0.16
ND
ND
ND
ND
ND
ND
0.03
ND
ND
Highest
(ppbv)
3.25
4.54
0.92
5.25
0.02
ND
1.80
0.03
0.08
117.00
1.62
1.36
ND
Central Tendency of Measured
Concentrations
Median
(ppbv)
1.31
1.36
0.63
1.37
0.02
0.04
0.08
0.02
0.03
0.11
0.28
0.03
0.02
Arithmetic
Mean
(ppbv)
1.49
1.70
0.66
1.83
0.01
0.04
0.19
0.02
0.03
5.86
0.35
0.21
0.02
Geometric
Mean
(ppbv)
7.33
1.45
0.65
1.45
0.01
0.04
0.08
0.02
0.03
0.33
0.29
0.07
0.02
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.69
1.10
0.08
1.32
0.00
0.00
0.37
0.00
0.01
23.43
0.27
0.36
0.00
Coefficient
of
Variation
0.46
0.64
0.12
0.72
0.06
0.00
1.90
0.10
0.34
4.00
0.79
1.74
0.00
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-36
-------
Table D-8 (Continued)
Summary Statistics for VOC Concentrations Measured at Hahnville, Louisiana (HALA)
(Based on 25 Valid Sampling Days)
Compound
\Iethylene Chloride
Trichlorotrifluoroethane
trans- 1 ,2-Dichloroethylene
1,1-Dichloroethane
Methyl tert-Butyl Ether
Methyl Ethyl Ketone
Chloroprene
cis- 1 ,2-Dichloroethylene
iromochloromethane
Chloroform
Ethyl tert-Butyl Ether
1 ,2-Dichloroethane
1,1,1- Trichloroethane
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
2
0
25
25
14
1
23
25
25
24
25
24
0
Frequency
of
Detections
92%
100%
0%
0%
44%
96%
8%
0%
0%
4%
0%
4%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.05
Highest
(ppbv)
1.37
0.30
ND
ND
5.14
1.93
1.44
ND
ND
0.05
ND
0.21
0.27
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.08
0.13
0.03
0.02
0.02
0.68
0.02
0.04
0.02
0.02«
0.03
0.04
0.07
Arithmetic
Mean
(ppbv)
0.17
0.13
0.03
0.02
0.32
0.79
0.11
0.04
0.02
0.02
0.03
0.05
0.09
Geometric
Mean
(ppbv)
0.11
0.13
0.03
0.02
0.05
0.65
0.02
0.04
0.02
0.02
0.03
0.04
0.08
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.26
0.04
0.00
0.00
1.05
0.39
0.34
0.00
0.00
0.01
0.00
0.03
0.06
Coefficient
of
Variation
1.58
0.31
0.00
0.00
3.23
0.50
3.05
0.00
0.00
0.32
0.00
0.73
0.69
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-37
-------
Table D-8 (Continued)
Summary Statistics for VOC Concentrations Measured at Hahnville, Louisiana (HALA)
(Based on 25 Valid Sampling Days)
Compound
benzene
Carbon Tetrachloride
tert-Amyl Methyl Ether
1 ,2-Dichloropropane
Ethyl Acrylate
Bromodichloromethane
rrichloroethylene
vlethyl Methacrylate
cis- 1 ,3-Dichloropropene
VIethyl Isobutyl Ketone
trans- 1 ,3-Dichloropropene
[ , 1 ,2-Trichloroethane
Toluene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
25
25
24
25
23
25
25
20
25
25
0
Frequency
of
Detections
100%
100%
0%
0%
4%
0%
8%
0%
0%
20%
0%
0%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
0.30
0.06
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.40
Highest
(ppbv)
2.40
0.13
ND
ND
0.09
ND
0.09
ND
ND
0.59
ND
ND
5.98
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.70
0.09
0.03
0.05
0.02
0.03
0.03
0.03
0.02
0.04
0.02
0.02
1.08
Arithmetic
Mean
(ppbv)
0.77
0.09
0.03
0.05
0.02
0.03
0.03
0.03
0.02
0.07
0.02
0.02
1.50
Geometric
Mean
(ppbv)
0.69
0.09
0.03
0.05
0.02
0.03
0.03
0.03
0.02
0.05
0.02
0.02
1.10
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.42
0.02
0.00
0.00
0.01
0.00
0.01
0.00
0.00
0.12
0.00
0.00
1.42
Coefficient
of
Variation
0.55
0.18
0.00
0.00
0.61
0.00
0.40
0.00
0.00
1.62
0.00
0.00
0.95
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-38
-------
Table D-8 (Continued)
Summary Statistics for VOC Concentrations Measured at Hahnville, Louisiana (HALA)
(Based on 25 Valid Sampling Days)
Compound
Dibromochloromethane
,2-Dibromoethane
n-Octane
Tetrachloroethylene
Chlorobenzene
Ithylbenzene
n-,p-Xylene
Bromoform
Styrene
1 , 1 ,2,2-Tetrachloroethane
9-Xylene
1,3,5- Trimethylbenzene
1,2,4- Trimethylbenzene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
25
25
0
16
25
0
0
25
0
25
0
I
0
Frequency
of
Detections
0%
0%
100%
36%
0%
100%
100%
0%
100%
0%
100%
96%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
ND
0.06
ND
ND
0.08
0.19
ND
0.03
ND
0.10
ND
0.09
Highest
(PPbv)
ND
ND
0.90
1.95
ND
0.59
1.54
ND
0.44
ND
0.74
0.24
0.67
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.02
0.03
0.13
0.05
0.02
0.15
0.37
0.06
0.06
0.03
0.20
0.07
0.18
Arithmetic
Mean
(ppbv)
0.02
0.03
0.27
0.17
0.02
0.19
0.46
0.06
0.09
0.03
0.23
0.09
0.21
Geometric
Mean
(ppbv)
0.02
0.03
0.16
0.08
0.02
0.17
0.40
0.06
0.07
0.03
0.20
0.08
0.18
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.00
0.00
0.19
0.39
0.00
0.11
0.30
0.00
0.09
0.00
0.14
0.05
0.13
Coefficient
of
Variation
0.00
0.00
0.90
2.27
0.00
0.60
0.64
0.00
1.01
0.00
0.60
0.54
0.64
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-39
-------
Table D-8 (Continued)
Summary Statistics for VOC Concentrations Measured at Hahnville, Louisiana (HALA)
(Based on 25 Valid Sampling Days)
f~\ 1
Compound
w-Dichlorobenzene
Chloromethylbenzene
>-Dichlorobenzene
>-Dichlorobenzene
• ,2,4-Trichlorobenzene
Hexachloro- 1 ,3-Butadiene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
24
25
21
24
24
24
Frequency
of
Detections
4%
0%
16%
4%
4%
4%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
ND
ND
ND
ND
ND
Highest
(ppbv)
0.05
ND
0.18
0.06
0.32
0.13
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.05
0.09
0.04
0.05
0.05
0.06
Arithmetic
Mean
(ppbv)
0.04
0.09
0.04
0.05
0.06
0.06
Geometric
Mean
(ppbv)
0.04
0.09
0.04
0.05
0.05
0.06
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.00
0.00
0.03
0.00
0.06
0.02
Coefficient
of
Variation
0.07
0.00
0.65
0.04
0.98
0.26
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one observation for each
successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central tendency concentrations for these
compounds should adequately represent long-term average concentrations, but the central tendency concentrations of the other compounds (in plain text) may be
influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in italics represent overall site-specific prevalent compounds over
80% for frequency only.
D-40
-------
Table D-9
Summary Statistics for VOC Concentrations Measured at North Little Rock, Arkansas (PARR)
(Based on 20 Valid Sampling Days)
Compound
Acetylene
Propylene
Dichlorodifluoromethane
Chloromethane
Dichlorotetrafluoroethane
Vinyl Chloride
!,3-Butadiene
Bromomethane
Chloroethane
Acetonitrile
Trichlorofluoromethane
Acrylonitrile
, 1-Dichloroethene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
0
0
20
20
12
20
20
16
/
20
20
Frequency
of
Detections
100%
100%
100%
100%
0%
0%
40%
0%
0%
20%
95%
0%
0%
Range of Measured
Concentrations
Lowest
(ppbv)
0.65
0.29
0.46
0.53
ND
ND
ND
ND
ND
ND
ND
ND
ND
Highest
(ppbv)
5.07
2.64
0.90
1.48
ND
ND
0.30
ND
ND
1.55
0.53
ND
ND
Central Tendency of Measured
Concentrations
Median
(ppbv)
1.71
0.84
0.63
0.70
0.02
0.04
0.03
0.02
0.03
0.11
0.28
0.03
0.02
Arithmetic
Mean
(ppbv)
2.13
0.98
0.65
0.80
0.02
0.04
0.08
0.02
0.03
0.26
0.29
0.03
0.02
Geometric
Mean
(ppbv)
1.87
0.84
0.64
0.77
0.02
0.04
0.05
0.02
0.03
0.15
0.25
0.03
0.02
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
1.17
0.58
0.11
0.27
0.00
0.00
0.08
0.00
0.00
0.39
0.09
0.00
0.00
Coefficient
of
Variation
0.55
0.60
0.18
0.33
0.00
0.00
1.10
0.00
0.00
1.51
0.32
0.00
0.00
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-41
-------
Table D-9 (Continued)
Summary Statistics for VOC Concentrations Measured at North Little Rock, Arkansas (PARR)
(Based on 20 Valid Sampling Days)
Compound
Methylene Chloride
Trichlorotrifluoroethane
trans- 1 ,2-Dichloroethylene
, 1 -Dichloroethane
Methyl tert-Butyl Ether
Methyl Ethyl Ketone
Chloroprene
cis- 1 ,2-Dichloroethylene
Bromochloromethane
Chloroform
Ethyl tert-Butyl Ether
1 ,2-Dichloroethane
Z, 1,1-Trichloroethane
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
1
0
20
20
20
0
20
20
20
16
20
20
1
Frequency
of
Detections
95%
100%
0%
0%
0%
100%
0%
0%
0%
20%
0%
0%
95%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
0.08
ND
ND
ND
0.08
ND
ND
ND
ND
ND
ND
ND
Highest
(ppbv)
6.85
0.26
ND
ND
ND
1.49
ND
ND
ND
0.07
ND
ND
0.09
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.20
0.10
0.03
0.02
0.02
0.66
0.02
0.04
0.02'
0.02
0.03
0.04
0.06
Arithmetic
Mean
(ppbv)
1.01
0.11
0.03
0.02
0.02
0.73
0.02
0.04
0.02
0.03
0.03
0.04
0.06
Geometric
Mean
(ppbv)
0.31
0.10
0.03
0.02
0.02
0.63
0.02
0.04
0.02
0.02
0.03
0.04
0.06
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
1.83
0.04
0.00
0.00
0.00
0.34
0.00
0.00
0.00
0.01
0.00
0.00
0.01
Coefficient
of
Variation
1.80
0.38
0.00
0.00
0.00
0.47
0.00
0.00
0.00
0.55
0.00
0.00
0.22
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-42
-------
Table D-9 (Continued)
Summary Statistics for VOC Concentrations Measured at North Little Rock, Arkansas (PARR)
(Based on 20 Valid Sampling Days)
Compound
benzene
Carbon Tetrachloride
tert-Amy\ Methyl Ether
1 ,2-Dichloropropane
ithyl Acrylate
Bromodichloromethane
rrichloroethylene
Methyl Meth aery late
cis- 1 ,3-Dichloropropene
Methyl Isobutyl Ketone
trans- 1 ,3-Dichloropropene
, 1 ,2-Trichloroethane
roluene
Prevalence of
Compound in Ambient
Aii-
Number of
Nondetects
0
0
20
20
20
20
20
20
20
15
20
20
0
Frequency
of
Detections
100%
100%
0%
0%
0%
0%
0%
0%
0%
25%
0%
0%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
0.26
0.02
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.26
Highest
(ppbv)
1.34
0.11
ND
ND
ND
ND
ND
ND
ND
0.14
ND
ND
3.22
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.58
0.08,
0.03-
0.05
0.02
0.03
0.03
0.03
0.02
0.04
0.02
0.02
0.78
Arithmetic
Mean
(ppbv)
0.63
0.08
0.03
0.05
0.02
0.03
0.03
0.03
0.02
0.05
0.02
0.02
0.97
Geometric
Mean
(ppbv)
0.57
0.08
0.03
0.05
0.02
0.03
0.03
0.03
0.02
0.04
0.02
0.02
0.79
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.29
0.02
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.03
0.00
0.00
0.74
Coefficient
of
Variation
0.47
0.27
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.58
0.00
0.00
0.76
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-43
-------
Table D-9 (Continued)
Summary Statistics for VOC Concentrations Measured at North Little Rock, Arkansas (PARR)
(Based on 20 Valid Sampling Days)
Compound
Dibromochloromethane
1 ,2-Dibromoethane
n-Octane
Tetrachloroethylene
Chlorobenzene
tthylbenzene
n-,p-Xylene
Bromoform
Styrene
1 , 1 ,2,2-Tetrachloroethane
y-Xylene
1, 3,5-Trimethylbenzene
,2,4-Trimethylbenzene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
20
20
0
12
20
0
0
20
0
20
0
1
0
Frequency
of
Detections
0%
0%
700%
40%
0%
100%
100%
0%
100%
0%
100%
95%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
ND
0.03
ND
ND
0.08
0.14
ND
0.04
ND
0.08
ND
0.10
Highest
(ppbv)
ND
ND
0.29
0.11
ND
0.63
1.76
ND
1.65
ND
0.85
0.53
1.77
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.02
0.03
0.09
0.05
0.02
0.18
0.42
0.06
0.07
0.03
0.24
0.08
0.23
Arithmetic
Mean
(PPbv)
0.02
0.03
0.10
0.06
0.02
0.23
0.56
0.06
0.18
0.03
0.30
0.12
0.34
Geometric
Mean
(PPbv)
0.02
0.03
0.09
0.05
0.02
0.20
0.45
0.06
0.10
0.03
0.24
0.10
0.25
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.00
0.00
0.06
0.02
0.00
0.16
0.44
0.00
0.36
0.00
0.21
0.11
0.38
Coefficient
of
Variation
0.00
0.00
0.60
0.38
0.00
0.69
0.78
0.00
1.99
0.00
0.72
0.92
1.12
ND = nondetect :
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-44
-------
Table D-9 (Continued)
Summary Statistics for VOC Concentrations Measured at North Little Rock, Arkansas (PARR)
(Based on 20 Valid Sampling Days)
Compound
Fn-Dichlorobenzene
Chloromethylbenzene
» -Dichlorobenzene
o-Dichlorobenzene
i ,2,4-Trichlorobenzene
Hexachloro- 1 ,3-Butadiene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
20
20
17
20
20
20
Frequency
of
Detections
0%
0%
15%
0%
0%
0%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
ND
ND
ND
ND
ND
Highest
(ppbv)
ND
ND
0.06
ND
ND
ND
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.05
0.09
0.04
0.05
0.05
0.06
Arithmetic
Mean
(ppbv)
0.05
0.09
0.04
0.05
0.05
0.06
Geometric
Mean
(ppbv)
0.05
0.09
0.04
0.05
0.05
0.06
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.00
0.00
0.01
0.00
0.00
0.00
Coefficient
of
Variation
0.00
0.00
0.19
0.00
0.00
0.00
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one observation for each
successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central tendency concentrations for these
compounds should adequately represent long-term average concentrations, but the central tendency concentrations of the other compounds (in plain text) may be
influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in italics represent overall site-specific prevalent compounds over
80% for frequency only.
D-45
-------
Table D-10
Summary Statistics for VOC Concentrations Measured at Rutland, Vermont (RUVT)
(Based on 31 Valid Sampling Days)
Compound
Acetylene
9ropylene
Jichlorodifluoromethane
Chloromethane
Dichlorotetrafluoroethane
Vinyl Chloride
1, 3 -Butadiene
Jromomethane
Chloroethane
Acetonitrile
Trichlorofluoro methane
Acrylonitrile
1,1-Dichloroethene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
0
0
29
31
2
29
31
16
0
31
31
Frequency
of
Detections
100%
100%
100%
100%
6%
0%
94%
6%
0%
48%
100%
0%
0%
Range of Measured
Concentrations
Lowest
(ppbv)
0.74
0.46
0.48
0.44
ND
ND
ND
ND
ND
ND
0.24
ND
ND
Highest
(ppbv)
5.86
2.50
1.40
0.87
0.02
ND
0.34
0.04
ND
20.43
0.67
ND
ND
Central Tendency of Measured
Concentrations
Median
(ppbv)
1.70
0.87
0.67
0.62
0.02
0.04
0.08
0.02
0.03
0.11
0.32
0.03
0.02
Arithmetic
Mean
(PPbv)
2.15
0.96
0.70
0.64
0.01
0.04
0.10
0.02
0.03
1.24
0.34
0.03
0.02
Geometric
Mean
(ppbv)
1.90
0.90
0.69
0.63
0.01
0.04
0.07
0.02
0.03
0.33
0.34
0.03
0.02
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
1.24
0.43
0.16
0.10
0.00
0.00
0.07
0.00
0.00
3.62
0.08
0.00
0.00
Coefficient
of
Variation
0.58
0.44
0.22
0.16
0.06
0.00
0.78
0.19
0.00
2.92
0.25
0.00
0.00
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-46
-------
Table D-10 (Continued)
Summary Statistics for VOC Concentrations Measured at Rutland, Vermont (RUVT)
(Based on 31 Valid Sampling Days)
Compound
Methylene Chloride
Trichlorotrifluoroethane
trans- 1 ,2-Dichloroethylene
1 , 1 -Dichloroethane
Methyl tert-Butyl Ether
Methyl Ethyl Ketone
Chloroprene
cis- 1 ,2-Dichloroethylene
Bromochloromethane
Chloroform
Ethyl tert-Butyl Ether
1 ,2-Dichloroethane
1, 1,1-Trichloroethane
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
3
0
31
31
2
0
31
31
31
27
31
31
0
Frequency
of
Detections
90%
100%
0%
0%
94%
100%
0%
0%
0%
13%
0%
0%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
0.04
ND
ND
ND
0.26
ND
ND
ND
ND
ND
ND
0.05
Highest
(ppbv)
0.86
0.12
ND
ND
0.55
1.36
ND
ND
ND
0.03
ND
ND
0.09
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.10
0.09
0.03
0.02
0.28
0.58 ,
0.02
0.04
0.02
0.02
0.03
0.04
0.06
Arithmetic
Mean
(ppbv)
0.15
0.09
0.03
0.02
0.28
0.62
0.02
0.04
0.02
0.02
0.03
0.04
0.06
Geometric
Mean
(ppbv)
0.11
0.09
0.03
0.02
0.22
0.56
0.02
0.04
0.02
0.02
0.03
0.04
0.06
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.16
0.02
0.00
0.00
0.15
0.29
0.00
0.00
0.00
0.00
0.00
0.00
0.01
Coefficient
of
Variation
1.05
0.17
0.00
0.00
0.53
0.47
0.00
0.00
0.00
0.17
0.00
0.00
0.17
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented irj bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-47
-------
Table D-10 (Continued)
Summary Statistics for VOC Concentrations Measured at Rutland, Vermont (RUVT)
(Based on 31 Valid Sampling Days)
Compound
benzene
Carbon Tetrachloride
tert-Amyl Methyl Ether
1 ,2-Dichloropropane
ithyl Acrylate
3romodichloromethane
frichloroethylene
Vlethyl Methacrylate
ds-l,3-Dichloropropene
Methyl Isobutyl Ketone
trans- 1 ,3-Dichloropropene
1,1,2-Trichloroethane
Toluene
Prevalence of
Compound in Ambient
Ail-
Number of
Nondetects
0
0
29
31
31
31
29
31
31
29
31
31
0
Frequency
of
Detections
100%
100%
6%
0%
0%
0%
6%
0%
0%
6%
0%
0%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
0.36
0.06
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.47
Highest
(ppbv)
1.52
0.12
0.06
ND
ND
ND
0.03
ND
ND
0.14
ND
ND
4.71
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.64
0.09
0.03
0.05
0.02
0.03
0.03
0.03
0.02
0.04
0.02
0.02
1.46
Arithmetic
Mean
(ppbv)
0.68
0.09
0.03
0.05
0.02
0.03
0.03
0.03
0.02
0.04
0.02
0.02
1.69
Geometric
Mean
(ppbv)
0.64
0.09
0.03
0.05
0.02
0.03
0.03
0.03
0.02
0.04
0.02
0.02
1.45
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.27
0.02
0.01
0.00
0.00
0.00
0.00
0.00
0.00
0.02
0.00
0.00
0.96
Coefficient
of
Variation
0.39
0.18
0.19
0.00
0.00
0.00
0.06
0.00
0.00
0.52
0.00
0.00
0.57
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-48
-------
Table D-10 (Continued)
Summary Statistics for VOC Concentrations Measured at Rutland, Vermont (RUVT)
(Based on 31 Valid Sampling Days)
Compound
Dibromochloromethane
1 ,2-Dibromoethane
n-Octane
Petrachloroethylene
Chlorobenzene
Ethylbenzene
n-,p-Xylene
Bromoform
Styrene
1 , 1 ,2,2-Tetrachloroethane
9-Xylene
1, 3, 5-Trimethylbenzene
1,2,4-Trimethylbenzene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
31
31
4
21
31
0
0
31
1
31
0
1
0
Frequency
of
Detections
0%
0%
57%
32%
0%
100%
100%
0%
97%
0%
100%
97%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
ND
ND
ND
ND
0. 10
0.24
ND
ND
ND
0. 13
ND
0.08
Highest
(ppbv)
ND
ND
0.20
0.07
ND
0.48
1.47
ND
0.37
ND
0.74
0.39
0.97
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.02
0.03
0.11
0.05
0.02
0.26
0.66
0.06
0.07
0.03
0.34 (
0.11
0.29
Arithmetic
Mean
(ppbv)
0.02
0.03
0.11
0.05
0.02
0.27
0.72
0.06
0.08
0.03
0.36
0.12
0.34
Geometric
Mean
(ppbv)
0.02
0.03
0.10
0.04
0.02
0.25
0.65
0.06
0.07
0.03
0.33
0.11
0.29
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.00
0.00
0.04
0.01
0.00
0.11
0.32
0.00
0.07
0.00
0.16
0.07
0.20
Coefficient
of
Variation
0.00
0.00
0.42
0.26
0.00
0.40
0.45
0.00
0.82
0.00
0.44
0.57
0.58
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-49
-------
Table D-10 (Continued)
Summary Statistics for VOC Concentrations Measured at Rutland, Vermont (RUVT)
(Based on 31 Valid Sampling Days)
Compound
>n-Dichlorobenzene
Chloromethylbenzene
» -Dichlorobenzene
o-Dichlorobenzene
1 ,2,4-Trichlorobenzene
Hexachloro- 1 ,3-Butadiene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
30
31
25
31
30
30
Frequency
of
Detections
3%
0%
19%
0%
3%
3%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
ND
ND
ND
ND
ND
Highest
(ppbv)
0.05
ND
0.04
ND
0.06
0.06
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.05
0.09
0.04
0.05
0.05
0.06
Arithmetic
Mean
(ppbv)
0.04
0.09
0.04
0.05
0.05
0.05
Geometric
Mean
(PPbv)
0.04
0.09
0.04
0.05
0.05
0.05
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.00
0.00
0.01
0.00
0.00
0.00
Coefficient
of
Variation
0.02
0.00
0.19
0.00
0.06
0.05
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one observation for each
successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central tendency concentrations for these
compounds should adequately represent long-term average concentrations, but the central tendency concentrations of the other compounds (in plain text) may be
influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in italics represent overall site-specific prevalent compounds over
80% for frequency only.
D-50
-------
Table D-ll
Summary Statistics for VOC Concentrations Measured at Texarkana, Arkansas (GREY)
(Based on 12 Valid Sampling Days)
/""f J
Compound
Acetylene
yropylene
Jichlorodifluoromethane
Chloromethane
Dichlorotetrafluoroethane
Vinyl Chloride
1,3 -Butadiene
Bromomethane
Chloroethane
Acetonitrile
Trichlorofluoromethane
Acrylonitrile
1,1-Dichloroethene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
0
0
12
12
12
10
11
7
0
9
12
Frequency
of
Detections
100%
100%
100%
100%
0%
0%
0%
17%
8%
42%
100%
25%
0%
Range of Measured
Concentrations
Lowest
(ppbv)
0.37
0.29
0.50
0.56
ND
ND
ND
ND
ND
ND
0.26
ND
ND
Highest
(Ppbv)
2.00
0.98
0.66
0.84
ND
ND
ND
0.17
0.55
8.95
0.44
1.01
ND
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.95
0.39
0.60
0.65
0.02
0.04
0.03
0.02
0.03
0.11
0.29
0.03
0.02
Arithmetic
Mean
(ppbv)
1.04
0.48
0.59
0.66
0.02
0.04
0.03
0.03
0.07
2.51
0.31
0.23
0.02
Geometric
Mean
(ppbv)
0.93
0.44
0.59
0.66
0.02
0.04
0.03
0.02
0.04
0.45
0.31
0.07
0.02
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.52
0.22
0.05
0.08
0.00
0.00
0.00
0.04
0.15
3.67
0.06
0.38
0.00
Coefficient
of
Variation
0.50
0.47
0.08
0.12
0.00
0.00
0.00
1.29
2.05
1.46
0.18
1.61
0.00
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-51
-------
Table D-ll (Continued)
Summary Statistics for VOC Concentrations Measured at Texarkana, Arkansas (GREY)
(Based on 12 Valid Sampling Days)
Compound
Methylene Chloride
rrichlorotrifluoroethane
trans- 1 ,2-Dichloroethylene
[,1-Dichloroethane
Methyl tert-Eutyl Ether
Methyl Ethyl Ketone
Chloroprene
cis- 1 ,2-Dichloroethylene
iromochloromethane
Chloroform
Ethyl tert-Butyl Ether
[ ,2-Dichloroethane
lj 1,1-Trichloroethane
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
12
12
12
0
12
12
12
12
12
12
0
Frequency
of
Detections
100%
100%
0%
0%
0%
100%
0%
0%
0%
0%
0%
0%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
0.11
0.07
ND
ND
ND
0.52
ND
ND
ND
ND
ND
ND
0.04
Highest
(ppbv)
0.54
0.10
ND
ND
ND
3.28
ND
ND
ND
ND
ND
ND
0.10
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.24
0.08
0.03
0.02
0.02
0.90
0.02
0.04
0.02
0.02
0.03
0.04
0.05
Arithmetic
Mean
(ppbv)
0.26'
0.08
0.03
0.02
0.02
1.18
0.02
0.04
0.02
0.02
0.03
0.04
0.06
Geometric
Mean
(ppbv)
0.23
0.08
0.03
0.02
0.02
0.97
0.02
0.04
0.02
0.02
0.03
0.04
0.05
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.13
0.01
0.00
0.00
0.00
0.84
0.00
0.00
0.00
0.00
0.00
0.00
0.02
Coefficient
of
Variation
0.50
0.12
0.00
0.00
0.00
0.72
0.00
0.00
0.00
0.00
0.00
0.00
0.30
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-52
-------
Table D-ll (Continued)
Summary Statistics for VOC Concentrations Measured at Texarkana, Arkansas (GREY)
(Based on 12 Valid Sampling Days)
Compound
lenzene
Carbon Tetrachloride
tert-Amy\ Methyl Ether
,2-Dichloropropane
ithyl Acrylate
Jromodichloromethane
Prichloroethylene
Vlethyl Methacrylate
cis- 1 ,3-Dichloropropene
Methyl Isobutyl Ketone
trans- \ ,3-Dichloropropene
1 , 1 ,2-Trichloroethane
roluene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
12
12
12
12
11
12
12
10
12
12
0
Frequency
of
Detections
100%
100%
0%
0%
0%
0%
8%
0%
0%
17%
0%
0%
100%
Range of Measured
Concentrations
Lowest
(ppbv)
0.26
0.05
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.16
Highest
(ppbv)
0.58
0.11
ND
ND
ND
ND
0.10
ND
ND
0.21
ND
ND
5.53
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.42
0.08
0.03
0.05
0.02
0.03
0.03
0.03
0.02
0.04
0.02
0.02
0.31
Arithmetic
Mean
(ppbv)
0.42
0.08
0.03
0.05
0.02
0.03
0.04
0.03
0.02
0.05
0.02
0.02
1.16
Geometric
Mean
(ppbv)
0.41
0.08
0.03
0.05
0.02
0.03
0.03
0.03
0.02
0.04
0.02
0.02
0.48
Variability in
Measured
Concentrations
Standard
Deviation
(PPbv)
0.10
0.02
0.00
0.00
0.00
0.00
0.02
0.00
0.00
0.05
0.00
0.00
1.99
Coefficient
of
Variation
0.23
0.26
0.00
0.00
0.00
0.00
0.56
0.00
0.00
0.95
0.00
0.00
1.71
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in'bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-53
-------
Table D-ll (Continued)
Summary Statistics for VOC Concentrations Measured at Texarkana, Arkansas (GREY)
(Based on 12 Valid Sampling Days)
Compound
Dibromochloromethane
[ ,2-Dibromoethane
i-Octane
Petrachloroethylene
Chlorobenzene
Ethylbenzene
n-,p-Xylene
iromoform
Styrene
1 , 1 ,2,2-Tetrachloroethane
y-Xylene
[ ,3,5-Trimethylbenzene
7,2,4- Trimethylbenzene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
12
12
2
11
12
0
1
12
1
12
1
3
1
Frequency
of
Detections
0%
0%
83%
8%
0%
100%
92%
0%
92%
0%
92%
75%
92%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
ND
ND
ND
ND
0.02
ND
ND
ND
ND
ND
ND
ND
Highest
(ppbv)
ND
ND
0.14
0.14
ND
0.49
0.61
ND
1.85
ND
0.34
0.11
0.35
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.02
0.03
0.07,
0.05
0.02
0.08
0.14
0.06
0.13
0.03
0.08
0.04
0.09
Arithmetic
Mean
(PPbv)
0.02
0.03
0.07
0.06
0.02
0.15
0.23
0.06
0.33
0.03
0.13
0.05
0.12
Geometric
Mean
(PPbv)
0.02
0.03
0.06
0.05
0.02
0.10
0.17
0.06
0.77
0.03
0.09
0.05
0.10
Variability in
Measured
Concentrations
Standard
Deviation
(PPbv)
0.00
0.00
0.03
0.03
0.00
0.14
0.20
0.00
0.52
0.00
0.11
0.02
0.09
Coefficient
of
Variation
0.00
0.00
0.48
0.45
0.00
0.97
0.88
0.00
7.55
0.00 '
0.84
0.47
0.74
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-54
-------
Table D-ll (Continued)
Summary Statistics for VOC Concentrations Measured at Texarkana, Arkansas (GREY)
(Based on 12 Valid Sampling Days)
Compound
w-Dichlorobenzene
Chloromethylbenzene
;-Dichlorobenzene
p-Dichlorobenzene
1 ,2,4-Trichlorobenzene
iexachloro- 1 ,3-Butadiene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
12
12
12
12
12
12
Frequency
of
Detections
0%
0%
0%
0%
0%
0%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
ND
ND
ND
ND
ND
Highest
(ppbv)
ND
ND
ND
ND
ND
ND
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.05
0.09
0.04
0.05
0.05
0.06
Arithmetic
Mean
(ppbv)
0.05
0.09
0.04
0.05
0.05
0.06
Geometric
Mean
(ppbv)
0.05
0.09
0.04
0.05
0.05
0.06
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.00
0.00
0.00
0.00
0.00
0.00
Coefficient
of
Variation
0.00
0.00
0.00
0.00
0.00
0.00
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one observation for each
successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central tendency concentrations for these
compounds should adequately represent long-term average concentrations, but the central tendency concentrations of the other compounds (in plain text) may be
influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in italics represent overall site-specific prevalent compounds over
80% for frequency only.
D-55
-------
Table D-12
Summary Statistics for VOC Concentrations Measured at Underbill, Vermont (UNVT)
(Based on 33 Valid Sampling Days)
Compound
icetylene
Propylene
Dichlorodifluoromethane
Chloromethane
Dichlorotetrafluoroethane
Vinyl Chloride
! ,3-Butadiene
Bromomethane
Chloroethane
\cetonitrile
Trichlorofluoromethane
Acrylonitrile
[,1-Dichloroethene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
0
0
28
33
32
31
33
28
0
30
33
Frequency
of
Detections
100%
100%
100%
100%
15%
0%
3%
6%
0%
15%
100%
9%
0%
Range of Measured
Concentrations
Lowest
(ppbv)
0.22
0.14
0.39
0.42
ND
ND
ND
ND
ND
ND
0.05
ND
ND
Highest
(ppbv)
7.57
0.51
0.75
0.98
0.02
ND
0.09
0.02
ND
5.85
0.58
0.30
ND
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.53
0.24
0.62
0.69
0.02
0.04
0.03
0.02
0.03
0.11
0.31
0.03
0.02
Arithmetic
Mean
(ppbv)
0.62
0.26
0.61
0.68
0.01
0.04
0.03
0.02
0.03
0.44
0.33
0.05
0.02
Geometric
Mean
(ppbv)
0.56
0.25
0.60
0.67
0.01
0.04
0.03
0.02
0.03
0.16
0.30
0.04
0.02
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.30
0.09
0.07
0.11
0.00
0.00
0.01
0.00
0.00
1.11
0.11
0.07
0.00
Coefficient
of
Variation
0.48
0.33
0.11
0.17
0.10
0.00
0.42
0.02
0.00
2.50
0.33
1.37
0.00
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-56
-------
Table D-12 (Continued)
Summary Statistics for VOC Concentrations Measured at Underbill, Vermont (UNVT)
(Based on 33 Valid Sampling Days)
Compound
VIethylene Chloride
rrichlorotrifluoroethane
trans- 1 ,2-Dichloroethylene
1 , 1 -Dichloroethane
Methyl tert-Butyl Ether
Methyl Ethyl Ketone
Chloroprene
cis- 1 ,2-Dichloroethylene
iromochloromethane
Chloroform
Ethyl tert-Butyl Ether
,2-Dichloroethane
'., 1,1-Trichloroethane
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
12
0
33
33
33
/
33
33
33
32
33
33
2
Frequency
of
Detections
64%
100%
0%
0%
0%
97%
0%
0%
0%
3%
0%
0%
94%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
0.05
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
Highest
(PPbv)
1.29
0.39
ND
ND
ND
1.06
ND
ND
ND
0.02
ND
ND
0.16
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.05
0.09
0.03;
0.02
0.02
0.39
0.02
0.04
0.02
0.02
0.03
0.04
0.06
Arithmetic
Mean
(ppbv)
0.13
0.10
0.03
0.02
0.02
0.43
0.02
0.04
0.02
0.02
0.03
0.04
0.06
Geometric
Mean
(ppbv)
0.08
0.09
0.03
0.02
0.02
0.36
0.02
0.04
0.02
0.02
0.03
0.04
0.06
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.23
0.05
0.00
0.00
0.00
0.21
0.00
0.00
0.00
0.00
0.00
0.00
0.02
Coefficient
of
Variation
1.71
0.54
0.00
0.00
0.00
0.50
0.00
0.00
0.00
0.06
0.00
0.00
0.35
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-57
-------
Table D-12 (Continued)
Summary Statistics for VOC Concentrations Measured at Underbill, Vermont (UNVT)
(Based on 33 Valid Sampling Days)
Compound
benzene
Carbon Tetrachloride
tert-Amy\ Methyl Ether
[ ,2-Dichloropropane
Ethyl Acrylate
B romodichloromethane
rrichloroethylene
VIethyl Methacrylate
cis- 1 ,3-Dichloropropene
VIethyl Isobutyl Ketone
trans- 1 ,3-Dichloropropene
1,1,2-Trichloroethane
Toluene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
33
33
32
33
33
32
33
31
33
33
0
Frequency
of
Detections
100%
100%
0%
0%
3%
0%
0%
3%
0%
6%
0%
0%
100%
Range of Measured
Concentrations
Lowest
(PPbv)
0.06
0.04
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.10
Highest
(PPbv)
0.40
0.12
ND
ND
0.16
ND
ND
0.07
ND
0.43
ND
ND
2.40
Central Tendency of Measured
Concentrations
Median
(PPbv)
0.21
0.09
0.03
0.05
0.02
0.03
0.03
0.03
0.02
0.04
0.02
0.02
0.20
Arithmetic
Mean
(PPbv)
0.22
0.08
0.03
0.05
0.02
0.03
0.03
0.03
0.02
0.05
0.02
0.02
0.36
Geometric
Mean
(PPbv)
0.20
0.08
0.03
0.05
0.02
0.03
0.03
0.03
0.02
0.04
0.02
0.02
0.25
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.08
0.02
0.00
0.00
0.02
0.00
0.00
0.01
0.00
0.07
0.00
0.00
0.45
Coefficient
of
Variation
0.37
0.22
0.00
0.00
1.01
0.00
0.00
0.22
0.00
1.42
0.00
0.00
1.26
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-58
-------
Table D-12 (Continued)
Summary Statistics for VOC Concentrations Measured at Underbill, Vermont (UNVT)
(Based on 33 Valid Sampling Days)
Compound
Dibromochloromethane
1 ,2-Dibromoethane
ra-Octane
Tetrachloroethylene
Ihlorobenzene
Ithylbenzene
m-,p-Xylene
Jromoform
Styrene
1 , 1 ,2,2-Tetrachloroethane
o-Xylene
1 ,3,5-Trimethylbenzene
1,2, 4-Trimethylbenzene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
32
32
15
31
33
5
0
33
8
32
1
1
1
Frequency
of
Detections
3%
3%
55%
6%
0%
85%
100%
0%
76%
3%
97%
79%
97%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
ND
ND
ND
ND
ND
0.02
ND
ND
ND
ND
ND
ND
Highest
(Ppbv)
0.02
0.03
0.16
0.05
ND
0.24
0.83
ND
0.11
0.04
0.43
0.44
0.71
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.02
0.03
0.05
0.05
0.02
0.06
0.09
0.06
0.04
0.03
0.06
0.04
0.06
Arithmetic
Mean
(ppbv)
0.02
0.02
0.05
0.05
0.02
0.07
0.12
0.06
0.05
0.03
0.07
0.05
0.09
Geometric
Mean
(ppbv)
0.02
0.02
0.05
0.05
0.02
0.07
0.10
0.06
0.04
0.03
0.06
0.04
0.07
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.00
0.00
0.02
0.01
0.00
0.04
0.13
0.00
0.02
0.00
0.07
0.07
0.12
Coefficient
of
Variation
0.04
0.04
0.44
0.20
0.00
0.55
1.13
0.00
0.48
0.10
0.94
1.41
1.33
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
D-59
-------
Table D-12 (Continued)
Summary Statistics for VOC Concentrations Measured at Underbill, Vermont (UNVT)
(Based on 33 Valid Sampling Days)
/"I J
Compound
ra-Dichlorobenzene
Chloromethylbenzene
; -Dichlorobenzene
9-Dichlorobenzene
,2,4-Trichlorobenzene
lexachloro- 1 ,3-Butadiene
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
32
33
31
32
32
32
Frequency
of
Detections
3%
0%
6%
3%
3%
3%
Range of Measured
Concentrations
Lowest
(ppbv)
ND
ND
ND
ND
ND
ND
Highest
(ppbv)
0.08
ND
0.09
0.11
0.41
0.27
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.05
0.09
0.04
0.05
0.05
0.06
Arithmetic
Mean
(PPbv)
0.05
0.09
0.04
0.05
0.06
0.06
Geometric
Mean
(ppbv)
0.05
0.09
0.04
0.05
0.05
0.06
Variability in
Measured
Concentrations
Standard
Deviation
(PPbv)
0.01
0.00
0.01
0.01
0.06
0.04
Coefficient
of
Variation
0.13
0.00
0.23
0.20
1.13
0.61
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one observation for each
successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central tendency concentrations for these
compounds should adequately represent long-term average concentrations, but the central tendency concentrations of the other compounds (in plain text) may be
influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in italics represent overall site-specific prevalent compounds over
80% for frequency only.
D-60
-------
APPENDIX E
1998/1999 SUMMARY TABLES FOR CARBONYL MONITORING
-------
Table E-l
Summary Statistics for Carbonyl Concentrations Measured at Baton Rouge, Louisiana (B2LA)
(Based on 18 Valid Sampling Days)
Compound
formaldehyde
^.cetaldehyde
Acrolein
Acetone
Jropionaldehyde
Crotonaldehyde
tutyr/Isobutyraldehyde
lenzaldehyde
sovaleraldehyde
faleraldehyde
Fblualdehydes
'iexaldehyde
2,5-Dimethylbenzaldehyde
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
5
0
0
13
0
0
5
0
4
0
16
Frequency
of
Detections
100%
100%
72%
100%
100%
28%
100%
100%
72%
100%
78%
100%
11%
Range of Measured
Concentrations
Lowest
(ppbv)
0.72
0.36
ND
0.07
0.07
ND
0.02
0.01
ND
0.01
ND
0.01
ND
Highest
(ppbv)
4.16
1.68
0.06
2.91
0.23
0.06
0.81
0.11
0.03
0.09
0.06
0.17
0.02
Central Tendency of Measured
Concentrations
Median
(ppbv)
7.57
0.69
0.01
0.72
0.70
0.00.
0.19
0.04
0.01
0.03
0.03
0.03
0.00
Arithmetic
Mean
(ppbv)
1.80
0.78
0.02
0.79
0.12
0.01
0.21
0.04
0.01
0. 03
0.03
0.04
0.00
Geometric
Mean
(ppbv)
7.59
0.72
0.01
0.48
0.11
0.00
0.75
0.04
0.01
0.03
0.02
0.03
0.00
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.97
0.34
0.02
0.74
0.05
0.02
0.19
0.03
0.01
0.02
0.02
0.04
0.00
Coefficient
of
Variation
0.54
0.44
0.99
0.93
0.45
1.72
0.90
0.58
0.71
0.53
0.73
0.97
1.71
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
E-l
-------
Table E-2
Summary Statistics for Carbonyl Concentrations Measured at Beulah, North Dakota (BUND)
(Based on 34 Valid Sampling Days)
Compound
formaldehyde
\cetaldehyde
Acrolein
Acetone
^ropionaldehyde
Crotonaldehyde
lutyr/Isobutyraldehyde
lenzaldehyde
sovaleraldehyde
?ale r -aldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
12
0
0
18
0
4
18
1
10
0
34
Frequency
of
Detections
100%
100%
65%
100%
100%
47%
100%
88%
47%
97%
71%
100%
0%
Range of Measured
Concentrations
Lowest
(ppbv)
0.51
0.35
ND
0.63
0.05
ND
0.02
ND
ND
ND
ND
0. 02
ND
Highest
(ppbv)
3.50
1.77
0.06
3.46
0.22
0.02
0.46
0.07
0.04
0.09
0.06
0.14
ND
Central Tendency of Measured
Concentrations
Median
(ppbv)
1.18
0.54
0.02
1.11
0.07
0.00
0.07
0.02
0.00
0.04
0.02
0.07
0.00
Arithmetic
Mean
(ppbv)
1.36
0.64
0.02
1.30
0.08
0.01
0.11
0.02
0.01
0.04
0.02
0.07
0.00
Geometric
Mean
(ppbv)
1.19
0.59
0.01
1.18
0.08
0.00
0.08
0.01
0.00
0.03
0.01
0.07
0.00
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.76
0.33
0.02
0.65
0.04
0.01
0.12
0.02
0.01
0.02
0.01
0.03
0.00
Coefficient
of
Variation
0.56
0.51
0.83
0.50
0.46
1.04
1.04
0.86
1.27
0.47
0.78
0.36
0.00
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
E=2
-------
Table E-3
Summary Statistics for Carbonyl Concentrations Measured at Brattleboro, Vermont (BRVT)
(Based on 31 Valid Sampling Days)
Compound
formaldehyde
\cetaldehyde
Acrolein
Acetone
^ropionaldehyde
Crotonaldehyde
3utyr/Isobutyraldehyde
Benzaldehyde
[sovaleraldehyde
/aleraldehyde
Tolualdehydes
iexaldehyde
2,5-Dimethylbenzaldehyde
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
13
0
0
17
0
1
12
0
2
0
28
Frequency
of
Detections
100%
100%
58%
100%
100%
45%
100%
97%
61%
700%
94%
100%
10%
Range of Measured
Concentrations
Lowest
(ppbv)
0.72
0.36
ND
0.18
0.05
ND
0.03
ND
ND
0.02
ND
0.02
ND
Highest
(ppbv)
3.55
1.51
0.09
2.62
0.24
0.12
0.28
0.16
0.05
0.11
0.07
0.17
0.01
Central Tendency of Measured
Concentrations
Median
(ppbv)
1.47
0.73
0.01
1.12
0.10
0.00
0.13
0.04
0.01
0.03
0.04
0.05
0.00
Arithmetic
Mean
(ppbv)
1.74
0.76
0.02
1.10
0.10
0.02
0.14
0.06
0.01
0.04
0.04
0.06
0.00
Geometric
Mean
(ppbv)
1.57
0.72
0.01
0.98
0.10
0.00
0.12
0.04
0.01
0.04
0.03
0.05
0.00
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.82
0.26
0.02
0.49
0.04
0.03
0.07
0.04
0.01
0.02
0.02
0.04
0.00
Coefficient
of
Variation
0.47
0.34
1.25
0.45
0.36
1.75
0.54
0.63
1.02
0.57
0.50
0.63
1.22
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
E-3
-------
Table E-4
Summary Statistics for Carbonyl Concentrations Measured at Burlington, Vermont (BUVT)
(Based on 32 Valid Sampling Days) s
Compound
formaldehyde
\cetaldehyde
Acrolein
Acetone
^ropionaldehyde
Crotonaldehyde
futyr/Isobutyraldehyde
lenzaldehyde
sovaleraldehyde
faler aldehyde
rolualdehydes
iex.aldeh.yde
2,5-Dimethylbenzaldehyde
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
11
0
0
18
1
0
15
1
0
0
21
Frequency
of
Detections
100%
100%
66%
100%
100%
44%
97%
100%
53%
97%
100%
100%
34%
Range of Measured
Concentrations
Lowest
(ppbv)
1.19
0.07
ND
0.08
0.02
ND
ND
0.03
ND
ND
0.01
0.01
ND
Highest
(ppbv)
6.52
1.67
0.20
2.26
0.25
0.11
0.59
0.16
0.04
0.07
0.05
0.11
0.02
Central Tendency of Measured
Concentrations
Median
(ppbv)
2.68
0.99
0.02
1.01
0.12
0.00
0.12
0.06
0.01
0.03
0.04
0.03
0.00
Arithmetic
Mean
(ppbv)
2.95
0.96
0.03
1.08
0.13
0.02
0.17
0.07
0.01
0.03
0.04
0.04
0.00
Geometric
Mean
(ppbv)
2.72
0.88
0.01
0.91
0.12
0.00
0.12
0.06
0.00
0.03
0.04
0.03
0.00
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
1.26
0.33
0.04
0.53
0.05
0.03
0.15
0.03
0.01
0.02
0.02
0.02
0.01
Coefficient
of
Variation
0.43
0.34
1.55
0.49
0.39
1.66
0.83
0.44
1.06
0.49
0.35
0.59
1.43
ND - nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
E 4
-------
Table E-5
Summary Statistics for Carbonyl Concentrations Measured at Camden, New Jersey (CANJ)
(Based on 29 Valid Sampling Days)
Compound
Formaldehyde
Icetaldehyde
\crolein
Acetone
Propionaldehyde
Crotonaldehyde
3utyr/Isobutyraldehyde
3enzaldehyde
rsovaleraldehyde
Valer -aldehyde
Tolualdehydes
^lexaldehyde
2,5-Dimethylbenzaldehyde
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
5
0
0
13
0
0
3
0
5
0
26
Frequency
of
Detections
100%
100%
83%
100%
100%
57%
100%
100%
90%
100%
83%
100%
13%
Range of Measured
Concentrations
Lowest
(ppbv)
1.51
0.82
ND
0.94
0.12
ND
0.21
0.02
ND
0.03
ND
0.03
ND
Highest
(ppbv)
8.75
3.25
0.20
3.73
0.74
0.12
1.23
0.23
0.11
0.78
0.09
0.29
0.02
Central Tendency of Measured
Concentrations
Median
(ppbv)
3.15
1.80
0.02
1.84
0.37
0.01
0.53
0.07
0.03
0.34
0.04
0.12 '
0.00
Arithmetic
Mean
(ppbv)
3.66
1.88
0.03
1.95
0.38
0.02
0.57
0.08
0.04
0.39
0.04
0.12
0.00
Geometric
Mean
(ppbv)
3.36
1.77
0.01
1.83
0.35
0.01
0.51
0.07
0.02
0.33
0.02
0.10
0.00
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
1.70
0.64
0.04
0.71
0.15
0.03
0.25
0.05
0.02
0.18
0.02
0.06
0.00
Coefficient
of
Variation
0.46
0.34
1.23
0.36
0.39
1.46
0.45
0.58
0.67
0.48
0.66
0.51
1.83
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
E-5
-------
Table E-6
Summary Statistics for Carbonyl Concentrations Measured at El Paso, Texas (EPTX)
(Based on 30 Valid Sampling Days)
Compound
formaldehyde
^.cetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/Isobutyraldehyde
Benzaldehyde
[sovaleraldehyde
?aler aldehyde
Tolualdehydes
iexaldehyde
2,5 -Dimethylbenzaldehyde
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
8
0
0
5
0
0
15
1
0
0
21
Frequency
of
Detections
100%
100%
73%
100%
100%
83%
100%
100%
50%
97%
100%
100%
30%
Range of Measured
Concentrations
Lowest
(ppbv)
L38
0.52
ND
0.22
0.08
ND
0.03
0.03
ND
ND
0.01
0.01
ND
Highest
(ppbv)
30.14
6.79
0.75
2.57
0.31
0.14
0.42
0.65
0.33
0.33
0.37
0.27
0.03
Central Tendency of Measured
Concentrations
Median
(ppbv)
3.91
1.51
0.02
1.33
0.17
0.03
0.17
0.09
0.01
0.05
0.07
0.05 •
0.00
Arithmetic
Mean
(ppbv)
7.54
2.28
0.11
1.37
0.19
0.04
0.18
0.17
0.04
0.08
0.09
0.09
0.01
Geometric
Mean
(ppbv)
5.26
L76
0.02
1.20
0.17
0.02
0.15
0.11
0.01
0.05
0.07
0.06
0.00
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
7.75
1.83
0.20
0.62
0.08
0.03
0.10
0.18
0.09
0.05
0.08
0.08
0.01
Coefficient
of
Variation
1.03
0.80
1.82
0.46
0.41
0.90
0.59
1.08
2.33
1.00
0.82
0.97
1.52
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
E-6
-------
Table E-7
Summary Statistics for Carbonyl Concentrations Measured at Garyville, Louisiana (GALA)
(Based on 29 Valid Sampling Days)
Compound
Formaldehyde
\cetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/Isobutyraldehyde
Benzaldehyde
tsovaleraldehyde
Valer aldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
12
0
0
19
2
0
1
0
1
2
25
Frequency
of
Detections
100%
100%
57%
100%
100%
32%
93%
100%
75%
100%
96%
93%
11%
Range of Measured
Concentrations
Lowest
(ppbv)
0.58
0.50
ND
0.25
0.77
ND
ND
0.02
ND
0.05
ND
ND
ND
Highest
(ppbv)
4.63
1.93
0.04
0.96
0.44
0.12
0.48
0.18
0.06
0.37
0.07
0.75
0.01
Central Tendency of Measured
Concentrations
Median
(ppbv)
2.16
1.09
0.01
0.49
0.24
0.00
0.20
0.06
0.02
0.27
0.04
0.09
0.00
Arithmetic
Mean
(ppbv)
2.32
1.08
0.01
0.51
0.24
0.01
0.23
0.07
0.02
0.20
0.04
0.09
0.00
Geometric
Mean
(ppbv)
2.14
1.03
0.01
0.48
0.23
0.00
0.15
0.06
0.01
0.18
0.02
0.06
0.00
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.94
0.34
0.01
0.20
0.08
0.03
0.14
0.04
0.02
0.08
0.02
0.04
0.00
Coefficient
of
Variation
0.40
0.32
1.00
0.39
0.32
2.05
0.60
0.53
0.85
0.41
0.60
0.48
1.67
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
E-7
-------
Table E-8
Summary Statistics for Carbonyl Concentrations Measured at Hahnville, Louisiana (HALA)
(Based on 21 Valid Sampling Days)
Compound
formaldehyde
Icetaldehyde
Acrolein
Acetone
^ropionaldehyde
Crotonaldehyde
tutyr/Isobutyraldehyde
Benzaldehyde
sovaleraldehyde
/aleraldehyde
Tolualdehydes
lexaldehyde
2,5-Dimethylbenzaldehyde
Prevalence of
Compound in Ambient
Ail-
Number of
Nondetects
0
0
1
0
0
16
3
2
6
I
4
I
19
Frequency
of
Detections
100%
100%
68%
100%
100%
27%
86%
91%
73%
95%
52%
95%
14%
Range of Measured
Concentrations
Lowest
(ppbv)
0.03
0.04
ND
0.03
0.01
ND
ND
ND
ND
ND
ND
ND
ND
Highest
(ppbv)
5.04
1.44
0.19
1.43
0.31
0.12
0.58
0.07
0.12
0.24
0.06
0.08
0.02
Central Tendency of Measured
Concentrations
Median
(ppbv)
1.32
0.55
0.01
0.60
0.10
0.00
0.13
0.02
0.01
0.04
0.02
0.05
0.00
Arithmetic
Mean
(ppbv)
1.72
0.67
0.02
0.62
0.11
0.01
0.15
0.03
0.02
0.06
0.02
0.05
0.00
Geometric
Mean
(ppbv)
1.27
0.53
0.01
0.33
0.09
0.00
0.07
0.02
0.01
0.04
0.01
0.04
0.00
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
7.20
0.41
0.04
0.51
0.08
0.03
0.14
0.02
0.03
0.06
0.02
0.02
0.00
Coefficient
of
Variation
0.70
0.61
1.97
0.81
0.70
2.41
0.92
0.64
1.34
1.01
0.83
0.44
1.77
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
£-8
-------
Table E-9
Summary Statistics for Carbonyl Concentrations Measured at North Little Rock, Arkansas (PARR)
(Based on 18 Valid Sampling Days)
Compound
Formaldehyde
\cetaldehyde
Acrolein
Acetone
^ropionaldehyde
Crotonaldehyde
Butyr/Isobutyraldehyde
Benzaldehyde
sovaleraldehyde
/aler 'aldehyde
rolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
9
0
0
9
0
0
9
3
0
0
17
Frequency
of
Detections
100%
100%
50%
100%
100%
50%
100%
100%
50%
83%
100%
100%
6%
Range of Measured
Concentrations
Lowest
(ppbv)
0.75
0.43
ND
0.46
0.06
ND
0.03
0.01
ND
ND
0.00
0.01
ND
Highest
(ppbv)
5.04
1.34
0.10
2.18
0.24
0.14
0.64
0.21
0.04
0.06
0.12
0.07
0.03
Central Tendency of Measured
Concentrations
Median
(ppbv)
1.50
0.70
0.01
7.25
0.77
0.00
0.09
0.04
0.00
0. 02
0.03
0.03
0.00
Arithmetic
Mean
(ppbv)
1.80
0.81
0.02
1.23
0.11
0.03
0.14
0.05
0.01
0.03
0.03
0.03
0.00
Geometric
Mean
(ppbv)
1.62
0.76
0.01
1.13
0.11
0.01
0.09
0.04
0.00
0.02
0.03
0.03
0.00
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
1.00
0.30
0.02
0.49
0.04
0.04
0.16
0.04
0.01
0.02
0.03
0.07
0.01
Coefficient
of
Variation
0.55
0.37
1.37
0.39
0.37
1.56
1.12
0.87
1.24
0.69
0.76
0.40
2.72
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
E-9
-------
Table E-10
Summary Statistics for Carbonyl Concentrations Measured at Rutland, Vermont (RUVT)
(Based on 28 Valid Sampling Days)
Compound
formaldehyde
\cetaldehyde
Acrolein
Acetone
^ropionaldehyde
Crotonaldehyde
Butyr/Isobutyraldehyde
Benzaldehyde
Isovaleraldehyde
faler aldehyde
Tolualdehydes
iexaldehyde
2,5-Dimethylbenzaldehyde
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
11
1
0
18
0
1
11
0
4
0
19
Frequency
of
Detections
100%
100%
61%
96%
100%
36%
100%
96%
61%
700%
86%
100%
32%
Range of Measured
Concentrations
Lowest
(ppbv)
0.64
0.30
ND
ND
0.05
ND
0.02
ND
ND
0.01
ND
0.00
ND
Highest
(ppbv)
5.11
1.65
0.15
2.31
1.36
0.10
0.48
0.15
0.03
0.10
0.08
0.11
0.02
Central Tendency of Measured
Concentrations
Median
(ppbv)
1.83
0.94
0.01
1.02
0.14
0.00
0.16
0.05
0.01
0.03
0.04
0.04
0.00
Arithmetic
Mean
(ppbv)
2.11
0.97
0.03
1.07
0.18
0.01
0.19
0.05
0.01
0.04
0.03
0.04
0.00
Geometric
Mean
(ppbv)
1.90
0.91
0.01
0.78
0.14
0.00
0.14
0.04
0.01
0.03
0.02
0.03
0.00
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
1.03
0.34
0.04
0.51
0.24
0.02
0.13
0.03
0.01
0.02
0.02
0.03
0.01
Coefficient
of
Variation
0.49
0.35
1.45
0.48
1.32
1.80
0.69
0.64
0.88
0.60
0.64
0.71
1.45
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
ErlO
-------
Table E-ll
Summary Statistics for Carbonyl Concentrations Measured at Texarkana, Arkansas (GREY)
(Based on 11 Valid Sampling Days)
Compound
formaldehyde
\cetaldehyde
Acrolein
\cetone
^ropionaldehyde
Crotonaldehyde
lutyr/Isobutyraldehyde
Benzaldehyde
sovaleraldehyde
/aler -aldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
6
0
1
4
0
0
8
1
2
0
11
Frequency
of
Detections
100%
100%
45%
100%
91%
64%
100%
100%
27%
97%
82%
100%
0%
Range of Measured
Concentrations
Lowest
(ppbv)
0.38
0.31
ND
0.41
ND
ND
0.02
0.01
ND
ND
ND
0.01
ND
Highest
(ppbv)
4.18
1.21
0.03
1.38
0.22
0.07
0.41
0.06
0.03
0.07
0.05
0.15
ND
Central Tendency of Measured
Concentrations
Median
(ppbv)
1.49
0.65
0.00
0.89
0.08
0.02
0.05
0.03
0.00
0.02
0.03
0.03
0.00
Arithmetic
Mean
(ppbv)
1.64
0.70
0.01
0.95
0.08
0.03
0.10
0.03
0.01
0.03
0.03
0.04
0.00
Geometric
Mean
(ppbv)
1.34
0.64
0.00
0.89
0.05
0.01
0.07
0.03
0.00
0.02
0.02
0.03
0.00
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
1.06
0.30
0.01
0.34
0.06
0.03
0.12
0.02
0.01
0.02
0.02
0.04
0.00
Coefficient
of
Variation
0.65
0.42
1.18
0.36
0.75
0.96
1.14
0.52
1.68
0.80
0.59
0.93
0.00
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
E-ll
-------
Table E-12
Summary Statistics for Carbonyl Concentrations Measured at Underbill, Vermont (UNVT)
(Based on 33 Valid Sampling Days)
Compound
Formaldehyde
^.cetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
3utyr/Isobutyraldehyde
3enzaldehyde
sovaleraldehyde
/aleraldehyde
folualdehydes
'iexaldehyde
2,5-Dimethylbenzaldehyde
Prevalence of
Compound in Ambient
Air
Number of
Nondetects
0
0
16
0
0
23
0
1
20
2
9
2
28
Frequency
of
Detections
100%
100%
52%
100%
100%
30%
100%
97%
39%
94%
73%
94%
15%
Range of Measured
Concentrations
Lowest
(ppbv)
0.45
0.24
ND
0.26
0.03
ND
0.01
ND
ND
ND
ND
ND
ND
Highest
(ppbv)
3.18
0.81
0.11
1.90
0.12
0.04
0.48
0.12
0.02
0.04
0.04
0.06
0.02
Central Tendency of Measured
Concentrations
Median
(ppbv)
0.85
0.44
0.00
0.84
0.06
0.00
0.08
0.02
0.00
0.02
0.01
0.02
0.00
Arithmetic
Mean
(ppbv)
1.06
0.46
0.01
0.90
0.06
0.01
0.12
0.03
0.00
0.02
0.02
0.02
0.00
Geometric
Mean
(ppbv)
0.91
0.44
0.00
0.84
0.06
0.00
0.08
0.02
0.00
0.01
0.01
0.02
0.00
Variability in
Measured
Concentrations
Standard
Deviation
(ppbv)
0.67
0.16
0.02
0.36
0.02
0.01
0.11
0.02
0.01
0.01
0.01
0.07
0.00
Coefficient
of
Variation
0.63
0.34
1.81
0.40
0.37
1.71
0.96
0.81
1.09
0.56
0.80
0.67
1.65
ND = nondetect
Notes: Summary statistics were calculated from a processed UATMP database, in which duplicate and replicate analyses were averaged to generate just one
observation for each successful sampling day. Program-wide prevalent compounds are presented in bold text. As Section 3.1.3 discusses, central
tendency concentrations for these compounds should adequately represent long-term average concentrations, but the central tendency concentrations of
the other compounds (in plain text) may be influenced by the number of nondetects and the magnitude of the detection limit. Compounds listed in
italics represent overall site-specific prevalent compounds over 80% for frequency only.
E-12
-------
APPENDIX F
1998/1999 VOC RAW MONITORING DATA
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Baton Rouge, LA (B2LA)
Yearly Report (September 1998 - September 1999)
SAMPLE SITES
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1.2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 -DICHLOROETHANE
1,1,1 -TRICHtOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m.p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 -TETRACHLOROETHANE
0-XYUENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0- DICHLOROBENZENE
1.2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
B2LA 14780
9/8/98
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
B2LA 14895
9/20/98
10/10/98
L8J0006/L8JV004
ppbv
0.76
0.61
0.63
0.87
ND
ND
0.04 U
ND
ND
96.36
0.36
ND
ND
0,10 U
0.10
ND
ND
ND
1.10
ND
ND
ND
ND
ND
ND
0,19
044
0.11
ND
ND
ND
ND
ND
0.28
ND
0.24
ND
ND
1.08
ND
ND
0.1S
ND
ND
0.28
0.68
ND
0.49
ND
0.39
0.09
0.24
ND
ND
ND
ND
ND
ND
B2LA 16064
10/2/98
10/22/98
L8JV018
ppbv
0.93
0.68
0.53
0.54
ND
ND
ND
ND
ND
42.56
0.22
ND
ND
ND
0.08
ND
ND
ND
0.59
ND
ND
ND
ND
ND
ND
0.05 U
0.56
0.05 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.03
ND
ND
0.83
ND
ND
0.70
2.71
ND
1.27
ND
1.84
2.34
6.85
ND
ND
ND
ND
ND
ND
B2LA1B126
10/14/98
10/30/98
L8J%008/L8KK024
ppbv
3.41
1-42
0.76
0.96
ND
ND
0.09
ND
ND
54.94
0.45
ND
ND
0,31
0.14
ND
ND
ND
1.60
ND
ND
ND
ND
ND
ND
0.20
1.17
0,07 U
ND
ND
ND
ND
ND
ND
ND
0.13
ND
ND
10.27
ND
ND
043
0.05 U
ND
0.59
1,84
ND
0.29
0.03 U
1.07
0.82
2.07
ND
ND
ND
ND
ND
ND
U = Under Detection Unit
ND -Not Detected
Tx98_99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Baton Rouge, LA (B2LA)
Yearly Report (September 1998 - September 1999)
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-OICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans • 1,7 - DICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2- DICHLOROETHANE
1,1,1 - TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 . TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-OIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLQROMETHYL8ENZENE
p- DICHLOROBENZENE
0 - DICHLOROBENZENE
1.24-TRICHLOROBENZENE
HEXACHLORO-14-8UTADIENE
B2LA 15167
11/1/98
tf/1t/98
L8KK021
ppbv
2.S2
0.97
0.57
0.58
NO
ND
0.11
ND
ND
43.18
0.26
ND
ND
0.08 0
0.10
ND
ND
ND
1.06
ND
ND
ND
ND
ND
ND
0.08
0.79
0.09
ND
ND
ND
ND
ND
ND
ND
0.10
ND
ND
145
ND
ND
0.18
ND
ND
0.34
048
ND
0.27
ND
0.57
0.40
0.90
ND
ND
0.03 U
ND
ND
ND
B2LA15175
11/7/98
11/19/98
L8KR016
ppbv
1.67
0.71
046
045
ND
ND
ND
ND
ND
3178
0.24
ND
ND
0.64
047
ND
ND
ND
1.14
ND
ND
ND
0.09
ND
ND
0.11
0.94
0.06 U
ND
ND
ND
ND
048
0.20
ND
0.19
ND
ND
5.60
ND
ND
042
0.07 U
ND
1.83
3.57
ND
0.75
ND
1.86
0.39
0.94
ND
ND
ND
ND
ND
ND
B2LA 15187
11/13/98
11/18/98
L8KR010/U8KR1015
ppbv
141
0.55
046
047
ND
ND
0.03 U
NP
ND
48.78
0.20
ND
ND
0.09 U
0.10
NP
ND
ND
0.86
ND
ND
ND
ND
NO
ND
0.05 U
0.52
0.08 U
ND
ND
ND
NP
ND
ND
ND
0.06 U
ND
ND
1.06
ND
ND
0.09
0.06 U
NO
0.24
0.62
ND
0.17
ND
0.34
0.12
0.31
ND
ND
ND
ND
ND
ND
B2LA 15203
11/19/98
11/30/98
L8K$016/L8LA015
ppbv
5.34
2.62
0.62
0.96
ND
ND
0.18
ND
ND
109.00
0.28
ND
ND
0.15
0.12
ND
ND
ND
1.16
ND
ND
ND
0.11
ND
ND
0.11
149
0.13
ND
ND
ND
ND
ND
0.19
ND
0.19
ND
ND
2.27
ND
ND
0.18
0.18
0.07
0.51
1.35
ND
0.54
ND
0.73
0.33
0.82
ND
ND
0.04 U
ND
ND
ND
U - Under Detection Limit
ND t=Not Detected
V = Void
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Baton Rouge, LA (B2LA)
Yearly Report (September 1998 - September 1999)
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
ACETYLENE
PROPVLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETOYLENE
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 - DICHLOROETHANE
1,1.1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-OIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m.p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
o-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHUOROMETHYLBENZENE
p - DICHLOROBENZENE
0- DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
S2LA 15213
11/25/98
12/8/98
L8LM014/L8LV012
ppbv
4.12
1.88
0.64
0.99
ND
ND
0.21
0.07
ND
91.22
0.29
ND
ND
0.14
0.12
ND
ND
ND
1.67
ND
ND
ND
0.09
ND
ND
0.11
1.46
0.11
ND
ND
ND
ND
ND
0.18
ND
5.21
ND
ND
2.35
ND
ND
0.17
0.07 U
ND
0.55
1.60
ND
0,49
ND
0.86
0.26
0.71
ND
ND
0.05 U
ND
ND
ND
B2LA 15243
12/1/98
12/9/98
L8LH018
ppbV
2.85
1.33
0.64
0,11
ND
ND
0.09
ND
ND
81.34
0.30
ND
ND
0.09 U
0.13
ND
ND
ND
1.15
ND
ND
ND
0.08
ND
ND
0.11
0.82
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.26
ND
ND
0.10
0.11
ND
0.30
0.80
ND
0.36
ND
0.44
0.19
0.46
ND
ND
0.03 U
NO
ND
ND
B2LA15367D1
1/30/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
B2LA 15368 02
1/30/99
2/11/99
L9BJ011/L9BQ006
ppbv
1.24
0,81
0.66
0.72
0.03
ND
0.09
ND
ND
52J2
0.32
ND
ND
0.29
0.14
ND
ND
NO
0.62
ND
ND
ND
ND
ND
ND
0.08
0.50
0.08
ND
ND
ND
ND
ND
NO
ND
0.07 U
ND
NO
1.00
ND
ND
0.08 U
ND
ND
0.23
0.59
ND
0.24
ND
0.30
0.12
0.28
ND
NO
ND
ND
NO
ND
U = Under Detection IMI
NO =Not Detected
V = Vold
3ol9
Tx98_99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Baton Rouge, LA (B2LA)
Yearly Report (September 1998 - September 1999)
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMQMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-OICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 • DtCHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL teiWUTYL ETHER
1,2-DICHLOROETHANE
1,1,1 .TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 • DICHLOROPROPANE
ETHYL ACRYLATE
BROMOPICHLOROMETHANE
TRICHLOROETHYLENE
METHYL WETHACRYLATE
els -1.3 - DICHLOROPROPENE
METHYL tSOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 • TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m.p-XYLENE
BROMOFORM
5TYRENE
1.1,2,2 -TETRACHLOROETHANE
o-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m-DICHLOROBENZENE
CHLOROMETHYLBENZENE
p-DICHLOROBENZENE
0 - DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
B2LA 15368 R2
1/30/99
2/12/99
L9BL009
ppbv
1.29
0.75
0.64
0.73
0.04
ND
0.08
ND
ND
$8.99
0.31
ND
ND
0.25
0.14
ND
ND
ND
0.67
ND
ND
ND
ND
ND
ND
0.09
049
0.10
ND
ND
ND
ND
ND
ND
ND
0.07 U
ND
ND
0.98
ND
ND
0.09 U
ND
ND
0.22
0.55
ND
0.24
ND
0,29
0.10
0.22
ND
ND
ND
ND
ND
ND
B2LA 15436
2/11/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
B2LA 1S437
2/1T/99
ppbv
V
V
V
V
V
V
V.
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V,
V
V
B2LA 16467
2/26/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
U = Under Detection Limit
ND =Not Detected
V = Vold
4 of 9
Tx98 99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Baton Rouge, LA (B2LA)
Yearly Report (September 1998 - September 1999)
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1.3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-OICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans • 1,2 - D1CHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL torWUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1.2- DICHLOROETHANE
1,1.t • TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMDDICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1,3 - DICHLOROPROPENE
METHYL iSOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
D1BROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
nt4>-XYLENE
BROMOFORM
STYRENE
1,1,2,2 -TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLORDMETHYLBENZENE
p- DICHLOROBENZENE
0 - DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
B2LA1S489
3/7/99
3/11/99
L9CJ022/L9CL010
ppbv
1.23
1,42
0.66
0.70
ND
0.26
ND
ND
ND
54.04
0.29
ND
ND
0.06 U
0.28
ND
ND
ND
0.77
NO
ND
ND
0.37
ND
0.32
0.07
0.75
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.67
ND
ND
0.12
ND
ND
0.17
0.40
ND
0.13
ND
078
0.07 U
0,20
ND
ND
ND
ND
ND
ND
B2LA 15509
3/13/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
B2LA 15532
3/19/99
3/24/99
L9CX008
ppbv
1.72
1.1J
0.60
0.7t
ND
ND
0.34
ND
ND
2.79
0.29
ND
ND
0.15
0.12
ND
ND
0.29
1.19
ND
ND
ND
ND
ND
ND
0.06
0.66
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.23
ND
ND
0.08 U
0.03 U
ND
0.2J
0.60
ND
0.09 U
ND
0.33
0.09
0.26
ND
ND
ND
ND
ND
ND
B2LA15S72
4/19/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V.
V
V
U = Under Detection Limit
ND-Not Detected
V = Vold
5of9
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Baton Rouge, LA (B2LA)
Yearly Report (September 1998 - September 1999)
SAMPLE SITES
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
ACETYLENE
PRQPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHAKE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-OICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - OICHLOROETHYLEME
1,1 - DICHLOROETHANE
METHYL tert-SUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
ciJ-1,2-OICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1^- DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,Z - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 • TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-OIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m.p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 -TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBEHZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
B2LA 15697
4/20/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
B2LA 15695
4/20/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
B2LA 15707
4/26/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
B2LA 16769
4/30/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
U = Under Detection Umlt
NO =Not Detected
V = Vold
6 o(9
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Baton Rouge, LA (B2LA)
Yearly Report (September 1998 - September 1999)
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
PILE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-OICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans • 1,2 - DICHLOROETHYLENE
1,1 • DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 - DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLDRDMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1,3 - DICHLOROPROPENE
METHYL tSOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p - XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
0- XYLENE
1,3.5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
B2LA1S7S6
5/2/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
B2LA 15778
5/25/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
B2LA 15815
6/4/99
6/9/99
L9FI009
ppbv
1.09
1.57
0.68
1.20
0.01 U
NO
0.05
ND
ND
0.70
1.87
ND
ND
0,19
0.10
ND
ND
0.07
0.66
NO
ND
ND
0.12
NO
ND
0.08
058
0.10
ND
ND
ND
ND
ND
ND
ND
0.15
ND
ND
0.72
ND
ND
0.13
0.03 U
ND
0.14
0.31
ND
0.10 U
ND
0.17
0.08 U
0.16
ND
ND
ND
ND
ND
ND
B2LA 15832
6/11/99
6/18/99
L9FQ014
ppbv
1.62
2.14
0.55
0,92
0.02 U
ND
OM
ND
ND
ND
0.24
ND
ND
0.10
0.14
ND
ND
0.21
0.57
ND
ND
ND
ND
ND
ND
0.06
0.76
0.17
ND
ND
ND
ND
0.04 U
ND
ND
ND
ND
ND
1.43
ND
ND
0.13
0.03 U
ND
0.27
0.75
ND
0.10
ND
0.36
0.12
0.31
ND-
ND
0.04 U
ND
ND
ND
U = Under Detection Limit
NO -Nol Detected
V = Void
1x98.99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Baton Rouge, LA (B2LA)
Yearly Report (September 1998 - September 1999)
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME.
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - V • DICHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1.2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYLtert-BUTYL ETHER
1,2-DICHLOROETHANE
1,1,1 -TR1CHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1»2. DICHLOROPROPANE
ETHYL ACRYLATE
8ROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL 1SOBUTYL KETONE
trans • 1,3 - DICHLOROPROPENE
1.1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-OIBROMOETHANE
K-OCTAKE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
0-XYLENE
1.3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m • DICHLOROBENZENE
CHLOROMETHYLBEHZENE
p- DICHLOROBENZENE
o- DICHLOROBENZENE
1,24-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
B2LA 16039
7/5/99
7/28/99
L9GI010
ppbv
1.56
3.41
0.71
2.28
0.07
ND
0.14
ND
0.24
ND
0.53
1.23
ND
0.26
0.59
ND
ND
ND
149
ND
ND
ND
ND
ND
ND
0,10
0.74
0.10
ND
ND
ND
ND
0.02 U
ND
ND
0.22
ND
ND
2.57
ND
ND
0.15
0.04 U
ND
0.19
049
ND
0.12
ND
0.26
0.08
0.21
ND
ND
0.03 U
ND
0.02 U
ND
B2LA 16133
7/23/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
B2LA 16246
7/29/99
8/11/99
L9HJ018
ppbv
1.15
5.00
0.74
2.S4
ND
ND
0.04 U
ND
0.15
ND
0.38
ND
ND
0.25
0.14
ND
ND
0.09
1.72
ND
ND
ND
0.09
ND
ND
0.09
0.55
0,12
ND
ND
ND
ND
ND
ND
ND
0.33
ND
ND
0.71
ND
ND
0.10
ND
ND
0.12
0.32
ND
0.05 U
ND
0.15
0.07 U
0,13
ND
ND
ND
ND
ND
ND
B2LA 16316
8/10/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
U = Under Detection Limit
ND =N« Detected
V = Vold
1x98.99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Baton Rouge, LA (B2LA)
Yearly Report (September 1998 - September 1999)
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYtONITRlLE
1,1-OICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
bans - V • D1CHLOROETHYLENE
1,1 • DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,2-OICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
12 - DICHLOROETHANE
1.1.1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL WETHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1.1 J! • TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-OIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p- DICHLOROBENZENE
o - DICHLOROBENZENE
1.2,4-TRICHLOROBENZENE
HEXACHLORO-1 ,3-BUTADIENE
B2LA 16475
8/22/99
9/2/99
L9IB010
ppbv
1.76
3.08
0.74
1.26
ND
0.0$ U
0.13
0.03 U
0.13
ND
0.32
0.25
ND
0.10
0.20
ND
ND
0.16
0.77
ND
ND
ND
0.28
NO
ND
0.22
0.72
0.12
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.14
NO
ND
0.15
0.03 U
ND
0.22
0.62
ND
0.11 U
ND
0.32
0.10
0.26
ND
ND
0.02 U
ND
ND
ND
B2LA 16695
9/5/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
B2LA 16721
9/15/99
9/23/99
L9IV015
ppbv
1.02
2.60
0.70
3.11
ND
ND
0.13
ND
ND
ND
044
ND
ND
O.S4
0.34
ND
ND
0.30
1.13
ND
ND
ND
ND
ND
0.49
O.OS U
OM
0.09 U
ND
ND
ND
ND
ND
ND
ND
NO
ND
ND
0.56
NO
ND
0.11
ND
NO
0.12
0.29
ND
0.07 0
ND
0.16
0.07 U
0.14
ND
ND
ND
ND
ND
ND
B2LA 16869
9/30/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V '
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
U = Under Detection Limit
ND =No( Detected
V = Void
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Beulah, ND (BUND)
Yearly Report (Feburary 1999 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETON1TRILE
TRICHLOROFLUOROMETHANE
ACRVLONITRILE
1.1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1.1 -DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1 ,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1 ,2 - DICHLOROETHANE
1,1.1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2-DICHLOROPROPANE
ETHYL ACRYLATE
BROMOOICHLOROMETHANE
TRICHLOROETHYLENE
M ETHYL M ETHACR YLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1.3 - DICHLOROPROPENE
1 ,1 » - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-OIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOR08ENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1 ,1 ,2,2 • TETRACHLOROETHANE
o - XYtENE
1 ,3,5-TRIM ETHYLBENZENE
1 ,2,4-TRIM ETHYLBENZENE
m-DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBEN2ENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
BUND 16374
2/3/99
2/11/99
L9BJQ12
ppbv
0.57
0.20
0.60
0.61
ND
ND
ND
NO
ND
1.2E
0.31
ND
ND
0.37
0.09
ND
ND
ND
NR
ND
ND
NO
ND
ND
ND
0,06
0.34
0.09
ND
ND
ND
NO
ND
NO
ND
ND
ND
NO
0.28
NO
ND
0.05 U
ND
ND
0.07 U
0.11
ND
0.05 U
ND
0.07
0.05 U
0.09
ND
ND
ND
NO
ND
ND
BUND 16407
2/13/99
2/23/99
L9BW012
ppbv
0.97
0,33
0.6B
0.60
ND
ND
ND
ND
ND
NR
0.53
ND
ND
0.69
0.08
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0.06
0.32
0.05 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.64
ND
ND
0,06 U
ND
ND
0.09 U
0.18
ND
0.09
ND
0,09
0.05 U
0.14
ND
ND
ND
ND
ND
ND
BUND 16429
2/17/99
2/23/99
L9BW013/CL016
ppbv
0.66
0,20
0.62
0.58
ND
ND
ND
ND
ND
NO
0.27
ND
ND
0.28
0.08
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0.06 •
0.27
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.20
ND
ND
ND
ND
ND
0.06 U
0.07 U
ND
0.04 U
ND
0,05
0.02 U
0.06 U
ND
NO
ND
ND
ND
ND
BUND 16441
2/23/99
3/4/99
L9CD014/CJ009
ppbv
0.71
0.17
0.55
0.56
ND
ND
ND
ND
ND
1.01
0.48
ND
ND
0,37
0.08
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0.03 U
0.23
0.05 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.25
ND
ND
ND
ND
ND
0.02 U
0,06 U
ND
ND
ND
0.02 U
ND
0.04 U
ND
NO
ND
ND
ND
ND
U = Under Detection Limit
ND-Not Detected
EC Estimated Value
Vc voided
NA = Not Analyzed
NR = Not Reported
BUNDM.W
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Beulah, NO (BUND)
Yearly Report ( Feburary 1999 - September 1999 ;
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
PILE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOM ETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1 ,2 - DICHLOROETHYLENE
1,1 - OICHLOROETHANE
M ETHYL tert-BUTYi, ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1 ,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tfilt-BUTYL ETHER
1,2 - DICHLOROETHANE
1,1,1 - TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - PICKLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1, 2- TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-DCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
o-XYLENE
1,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIM ETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
BUND 16451
3/1/39
3/1Q/99
L9CJ013
ppbv
0.57
0.21
0.63
0.61
NO
ND
ND
ND
ND
1-52
0.29
ND
ND
0.53
0.08
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0.05 U
0.21
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.22
ND
ND
0,36
ND
ND
0.05 U
0.10
ND
0.04 U
ND
O.OS
0.04 U
0.11
ND
ND
ND
ND
ND
ND
BUND 15497
3/7/99
3/13/99
L9CL017
ppbv
0.66
0,18
0.57
0.86
ND
NO
ND
ND
ND
1.45
0.27
ND
ND
0.41
0.07
ND
ND
ND
NR
ND
ND
ND
ND
NO
ND
0.06
0.23
0.07 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.17
ND
ND
ND
ND
ND
0.05 U
0.07 U
ND
0.03 U
ND
0.06
0.03 U
0.08 U
ND
ND
ND
ND
ND
ND
BUND 15502
3/13/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
-V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
•V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
BUND 16637
3/13/83
3/25/99
L9CXQ16
ppbv
0.73
0.13
0.59
0.56
ND
ND
ND
ND
ND
2.73
0.29
ND
ND
0.48
0.09
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0.04 U
0.23
0.06 U
ND
NP
ND
ND
ND
ND
ND
ND
ND
ND
0.14
ND
ND
ND
ND
ND
O.OG U
0.07 U
ND
0.02 U
ND
0.04
0.03 U
0.04 U
ND
ND
ND
ND
ND
ND
U = Under Detection Limit
NO = Not Detected
E = Estimated Value
V = Voided
NA = Not Analyzed
NR = Not Reported
BUND98.89
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Beulah, ND (BUND)
Yearly Report ( Feburary 1999 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
PILE NAME
UNITS
ACETYLENE
PRQPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1 ,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1 ,2 - OICHLOROETHYLENE
1,1 -DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1 ,2-DICHLOROETH YLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tftft-BUTYL ETHER
1,2 - DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1 ,2 - PICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACR YLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TfrlCHLOROETHANE
TOLUENE
DIBROMOCHLOROM ETHANE
1,2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1 ,1 ,2,2 • TETRACHLOROETHANE
o - XYLENE
1.3,5-TRIMETHYLBENZENE
1 ,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROM ETHYLBENZENE
p - DICHLOROBENZENE
o - DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1 ,3-BUTADIENE
BUND 1 $640 D1
3/19/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
BUND 16542 02
3/19/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
BUND 15S70
3/25/99
4/22/99
L9DU013
ppbv
0.65
0.21
0.61
0.64
ND
ND
ND
ND
ND
5.60
0.31
NO
ND
0,36
0.08
NO
ND
ND
NR
ND
ND
ND
NO
ND
ND
D.06
0.25
0.06 U
ND
NO
ND
no
ND
ND
ND
NO
ND
ND
0.21
ND
ND
0.05 U
ND
NO
0.06 U
0.10
ND
0.05 U
ND
0.06
0.05 U
0.08 U
ND
ND
ND
ND
ND
NO
BUND 16640
3/31/99
4/22/99
L9DV012
ppbv
0.60
0.34
0.66
0.66
ND
ND
ND
ND
ND
1.54
0.40
ND
ND
1,27
0.09
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0.07
0.29
0.09 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.50
ND
ND
0.09
ND
ND
0.10
0.18
ND
0.08 U
ND
0.09
0.05 U
0.14
ND
ND
ND
ND
ND
ND
U = Under Detection Umlt
NO = Not Detected
E ° Estimated Value
V = Voided
NA - Not Analyzed
NR = Not Reported
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Beulah, ND (BUND)
Yearly Report ( Feburary 1999 - September 1999 )
SAMPLE SIT6#
SAMPLE DATE
ANALYSIS DATE
PILE NAME
UNITS
ACETYLENE
PROPVUENE
DICHLORODIFLUOROMETHANE
CHLOROM ETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETON1TRILE
TRICHLOROFLUOROMETHANE
ACRYtONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DIGHLOROETHYLENE
1,1 -DICHLOROETHANE
METH YL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1 ,2-DICHLOROETH YLENE
BROMOCHUOROMETHANE
CHLOROFORM
ETHYL t«rt-BUTYL ETHER
1,2 - DICHLOROETHANE
1,1.1 • TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 • DJCHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1 ,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 • DICHLOROPROPENE
1,1 ,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m.p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
0 - XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIM ETHYLBENZENE
m - DICHLOROBENZENE
CHLOROM ETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1 ,3-BUTADIENE
BUND 16646
4/6/99
4/22/99
L9DV013
ppbv
1.11
0.41
1.04
0.62
ND
ND
0.03 U
ND
ND
1.BO
0.40
ND
ND
0.41
0.08
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0.13
0.37
0.06 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.80
ND
ND
0,09 U
0.07 U
ND
0.13
0.33
ND
0.17
ND
0.17
0.08
0.19
ND
ND
ND
ND
ND
ND
BUND 16637
4712/99
4/22/99
L9DV011
ppbv
0.81
0.34
0.69
0.64
ND
ND
ND
ND
ND
3.77
0.51
ND
ND
1.27
0.10
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0.06
0.29
0.06 U
ND
ND
ND
ND
ND
ND
ND
0.38
ND
ND
1.05
ND
ND
0.09 U
ND
ND
0.24
0.60
ND
0.10 U
ND
0.20
0.04 U
0.11
ND
ND
ND
ND
ND
ND
BUND 16682 D1
4/18/99
5/11/99
L9EJ018
ppbv
0.60
0.29
0.67
0.58
ND
ND
ND
ND
ND
ND
1.07
ND
ND.
0,20
0.09
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0.07
0.31
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.37
ND
ND
0.05 U
ND
ND
0.07 U
0,13
ND
0.04 U
ND
0.08
0.04 U
0.08 U
ND
ND
ND
ND
ND
ND
BUND1S682R1
4/18/99
5/12/99
L9EL011
ppbv
0.71
0.31
0.73
0.62
ND
ND
ND
ND
ND
O.B5
1.49
ND
ND
0.21
0.09
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0,06
0.32
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.46
ND
ND
0,05 U
ND
ND
0.08 U
0.16
ND
0.05 U
ND
0.06
0.05 U
0.08 U
ND
ND
ND
ND
ND
ND
U = Under Detection Liml!
ND = Not Detected
E - Estimated Value
V = Voided
NA e Not Analyzed
NR - Not Reported
BUN09B_89
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Beulah, ND (BUND)
Yearly Report ( Feburary 1999 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
PILE NAME
UNITS
ACETYLENE
PROPVLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOM ETHANE
CHLOROETHANE
ACETON1TRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
M ETHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans -1,2- DICHLOROETHYLENE
1,1 -DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1 ,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETH ER
1,2 - DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIOE
tert-AMYL METHYL ETHER
1,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROM ETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - T«ICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-DCIANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m.p-XYLeNE
BROMOFORM
STYRENE
1,1,2,2 -TETRACHLOROETHANE
0-XYUENE
1 ,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p • DICHLOROBENZENE
0- DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
BUND 16684 D2
4/18/99
6/11/39
L9EJ019
ppbv
0.56
0.34
0.63
0.71
ND
ND
ND
ND
ND
0,B7
0.31
ND
ND
0.40
0.10
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
o.oa
0.28
0.08 U
ND
ND
ND
ND
ND
NO
ND
ND
ND
ND
0.22
NO
ND
0.06 U
ND
ND
0.06 U
0.11
ND
0.04 U
ND
0,07
0.04 U
0.07 U
ND
ND
ND
ND
ND
ND
BUND 16684 R2
4/18/99
6/12/99
L9EL012
ppbv
O.S8
0,32
0.61
0.64
ND
ND
ND
ND
ND
0.97
0.32
ND
ND
0.36
0.10
ND
ND
ND
NR
ND
ND
NO
ND
ND
ND
0.06
0.27
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.22
ND
ND
0.07 U
ND
ND
0.06 U
0,10
ND
0.04 U
ND
0.06
0.04 U
0.07 U
ND
ND
ND
ND
ND
ND
BUND 15705
4/24/99
ppbv
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA.
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
BUND 16712
4/30/99
6/19/99
L9ER016
ppbv
0.57
0.31
0.69
0.66
ND
ND
ND
ND
ND
ND
0.78
ND
ND
0.93
0.09
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0.07
0.21
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.33
ND
ND
0,0$ U
ND
ND
0.07 U
0.11
ND
0.03 U
ND
0,07
0.04 U
0.07 U
ND
ND
ND
ND
ND
ND
U » Under Detection Urrtl
ND = Nol Detected
E = Estimated Value
V = Voided
NA = Not Analyzed
NR • Not Reported
BUND98_99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Beulah, ND (BUND)
Yearly Report ( Feburary 1999 - September 1999 )
SAMPLE SITES
SAMPLE BATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PRpPYLc-NE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITR1LE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans -1,2 - DtCHLOROETHYLENE
1,1 -DICHLOROETHANE
METHYL terrt-BUTYL ETHER
METHYLETHYLKETONE
CHLOROPRENE
cis-1 ,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 - DICHLOROETHANE
1.1,1 - TRJCHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - OICKLOROPROPANE
ETHYL ACRYLATE
BROMOOICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METH ACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1 ,3 - DICHLOROPROPENE
1*1 ,2- TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
ra.p-XYLENE
BROMOFORM
STYRENE
1 .1,2,2 - TETRACHLOROETHANE
o-XYLENE
1,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIM ETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1.J-BUTADIENE
BUND 16727
6/6/99
ppbtf
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
BUND 16729
6/6/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
BUND 16773
5/18/99
5/26/99
L9EZ016
ppbv
0.66
9.40
0.97
0.69
ND
ND
ND
ND
NO
ND
0.33
ND
ND
0.64
0.10
ND
ND
ND
NR
ND
ND
NO
ND
ND
ND
0.08
0.21
0.10
ND
ND
ND
ND
ND
ND
ND
0.61
ND
ND
0.42
ND
ND
0.07 U
ND
ND
0.14
0,28
ND
0.09 U
ND
0.17
0.08
0.19
ND
ND
ND
ND
ND
ND
BUND 15771
6/24/99
5/26/93
L9EZ017
ppbv
0.48
0.33
0.16
0.64
ND
ND
ND
ND
ND
ND
0.40
ND
ND
0.42
0.10
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0.05 U
0.49
0X19
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.56
ND
ND
0.1Q
ND
ND
0.11
0.22
ND
0.03 U
ND
0,12
0.04 U
0.09 U
ND
ND
ND
ND
ND
ND
U = Under Detection Until
ND = Not Detected
E = Estimated Value
V-Voided
NA= Not Analyzed
NR = Not Reported
-------
1998/1999 UATMP (Urban Air Toxics Mi
Yearly Report ( Feburary
SAMPLE SITS*
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENB
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETOWTR1LE
TRICHLOROFLUOROMETHANE
ACRYLONFTRILE
1,1-DICHLOROETHENE
WETHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL t«t-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tett-BUTYL ETHER
1 ,2 - DICHLOROETH ANE
1,1,1 - TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 -OICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
VI ,2 -TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1.2-DIBROMOETHANE
M-OCTANE
TETRACHLOROETHYLENE
CHLOR08ENZENE
ETHYLBENZENE
rn.p-XYLENE
BROMOFORM
STYRENE
1 ,1 ,2,2 - TETRACHLOROETHANE
o-XYLENE
1,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIM ETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 -DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTAD1ENE
BUND 16834
6/11/99
6/17/99
L9FQ013
ppbv
1.20
0.46
1.06
0.63
0.01 U
NO
0.02 U
NO
ND
2.31
0.33
NO
ND
0.41
0.10
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0.16
0.25
0.08 U
ND
ND
ND
ND
ND
ND
ND
HO
ND
ND
1.14
ND
ND
D.10
0.04 U
NO
0.14
0.21
ND
0.11
ND
0.13
0.05 U
0.10
ND
ND
0.02 U
ND
0.01
ND
anitoring Program) - Beulah, ND (BUND)
1999- September 1999)
BUND 1S899
6/17/99
6/24/99
L9FW014
ppbv
0.37
0.34
0.57
0.65
0.02 U
ND
ND
ND
ND
1.45
0.32
0.16
ND
0.59
0.14
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0.06
0.13
0.08 U
ND
NP
ND
ND
ND
ND
ND
0.10
ND
ND
0.22
ND
ND
0.10
ND
ND
0.06 U
0,11
ND
0.06 U
ND
0.07
0.04 U
0.08 U
ND
ND
ND
ND
ND
ND
BUND 15929
6/23/99
6/24799
L9FS014
ppbv
0.74
• 0.36
0.69
0.83
0.11
0.11
ND
015
0.14
1.09
0.56
ND
0.14
2.85
0.46
ND
0.09
ND
NR
ND
ND
ND
0.11
ND
0.12
0.18
0.32
0.09
ND
ND
ND
ND
0.09
ND
ND
ND
ND
0.11
1.32
ND
0.08
0.20
0.09 U
0.10
0.18
0,34
ND
0.11
0.05 U
0.19
0.11
0.15
0.05 U
ND
0.05 U
0.05 U
0.01 U
0.03 U
BUND 16969
C/29/99
7/2/99
L9GB014
ppbv
0.63
0,27
0.57
0.62
0.02 U
ND
ND
0.02 U
ND
ND
0.32
ND
ND
D.33
0.27
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0.07
0.21
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.48
ND
ND
Q.OB U
ND
ND
0.07 U
0.14
ND
O.OS U
ND
0,07
0.04 U
0.07 U
ND
ND
ND
ND
ND
ND
U » Under Detection Unit
ND = Not Detected
E = Estimated Value
V* Voided
MA = Not Analyzed
NR* Not Reported
BUND9S_GB
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Beulah, ND (BUND)
Yearly Report ( Feburary 1999 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PKOPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETOWTRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METH YLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1 ,2 - DICHLOROETH YLENE
1,1-DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1 ,2-DICHLOROETH YLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL ttsft-BUTYL ETHER
1,2 - DICHLOROETH ANE
1.1,1 - TRTCHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1 ,2 - OICHLOROPROPANE
ETHYL ACRYLATE
BROMOD1CHLOROMETHANE
TRICHLOROETHYLENE
METHYL METH ACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
t ,1 .2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
W,p-XYLENE
BROMOFORM
STYRENE
1,1,2.2- TETRACHLOROETHANE
o-XYUENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TfHMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-8UTADIENE
BUND 16003
7/5/99
7/20/99
L9GT014
ppbv
0.34
0.33
0.74
0.59
0.01 U
NO
ND
ND
ND
0.91
0.47
NO
ND
0.50
0.11
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0.07
0.19
0.08 U
ND
ND
ND
ND
ND
ND
ND
0.10
ND
ND
0.30
ND
ND
0.09
ND
ND
0.06 U
0,11
ND
0,06 U
ND
0.07
0.04 U
0.07 U
ND
ND
ND
ND
ND
ND
BUND 16135
7/17/99
7/28/99
L9GI017
ppbv
0.29
0.3S
0.65
0.67
ND
ND
ND
ND
ND
0.91
0.37
0.10
ND
0.57
0.10
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0.07
0.23
0.08 U
ND
ND
ND
ND
0.11
ND
ND
ND
ND
ND
0.34
ND
ND
0.09 U
0.14
ND
0.06 U
0,12
ND
0.06 U
ND
0.08
0.04 U
0.08 U
ND
ND
ND
ND
ND
ND
BUND 16146
7/23/99
8/11/99
L9HJ013
ppbv
0.45
0.49
0.72
0,77
ND
ND
ND
ND
ND
ND
0.45
ND
ND
0.54
0.11
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0.06
0.19
0.11
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.31
ND
ND
0.08 U
ND
ND
0.07 U
0.13
ND
0.07 U
ND
0.09
0.04 U
0.09
ND
ND
ND
ND
ND
ND
BUND1S203
7/29/99
8/11/99
L9HJ020
ppbv
0.80
1.14
0.69
0.70
ND
ND
ND
ND
0.29
ND
0.43
ND
ND
0.97
0.10
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0.06
0.56
0.10
ND
ND
ND
ND
ND
NO
ND
0.22
ND
NO
0.95
ND
ND
0,14
ND
ND
0.15
0.31
ND
0.16
ND
0.14
0.05 U
0.11
ND
ND
ND
NO
ND
NO
U o Under Detection Limit
ND = Not Detected
E ° Estimated Value
V = Voided
NA = Not Analyzed
NR = Not Reported
BUND98_99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Beulah, ND (BUND)
Yearly Report ( Feburary 1999 - September 1999 )
SAMPte SITES
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
AQETONITWLE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1 ,2 - DICHLOROETH YLENE
1,1 -DICHLOROETHANE
METHYL tert-euTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
CIS-1.2-DICHLOROETHYLENE
BROMQCHLOROMETHANE
CHLOROFORM
ETHYL tett-BUTYL ETHER
1.2 -DICHLOROETHANE
1 ,1 ,1 - TRICHLOROETHANE
BENZENE
CARBON TETRACHLOR10E
tert-AMYL METHYL ETHER
1.2 - P1CHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1.3 - OICHLOROPROPENE
1>1.2 -TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-9CTANB
TETRACHLOROETHYLENE
CHLORO8EN2ENE
ETHYLBENZENE
m>P-XYLENE
BROMOFORM
STYRENE
1 .1,2,2 - TETRACHLOROETHANE
a - X YLENE
1,3.5-TRIMETHYLBENZENE
1 A4-TR1M ETHYLBENZENE
m - DICHLOROBENZENE
CHLQRQMETHYLBENZENE
p • DICHLOROBENZENE
0 - DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1 ,3-BUTADIENE
BUND 16284
8/4/99
8/17/99
L9HP010
ppbv
0.41
0.31
0.68
0.63
ND
ND
ND
ND
ND
0.77
0.37
ND
ND
0.35
0.15
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0.06
0.19
0.07 0
ND
NO
ND
ND
ND
ND
ND
NO
ND
ND
0.25
ND
ND
0.10
ND
NO
0.06 U
0.12
ND
0.07 U
ND
0.07
0.05 U
0.08 U
ND
NO
ND
ND
ND
ND
BUND 16914
8/10/99
8/17/99
L9WP021
ppbv
0.78
0.94
O.B2
0,66
ND
ND
ND
ND
0.13
0.99
0.41
ND
ND
0,58
0.09
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0.09
0.47
0.08 U
ND
NP
ND
ND
ND
ND
ND
0.17
ND
ND
1.19
ND
ND
0.13
0.02 U
ND
0.19
0.40
ND
0.18
ND
0.20
0.06 U
0.14
ND
ND
ND
ND
ND
ND
BUND 16359
8/16/99
ppbv
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
BUND 16440
8/22/99
9/7/99
L9IGOOS
ppbv
0.41
0.39
0.59
O.S6
ND
NO
ND
ND
ND
1tt?
0.29
ND
ND
0.40
0.13
NO
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.05 U
0.21
0.08 U
ND
NO
ND
NO
ND
ND
ND
NO
ND
NO
0.31
ND
ND
0.10
ND
ND
0.07 U
0.14
ND
0.08 U
ND
0.09
0.05 U
0.09
ND
ND
ND
ND
ND
ND
U = Under Detection Unit
NO:Not Detected
E = Estimated Value
V = Voided
NA = Not Analyzed
NR <= Not Repotted
BUND98_99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Beulah, ND (BUND)
Yearly Report ( Feburary 1999 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
PILE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1 ,2 - DICHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1 ,2-DICHLOROETH YLENE
BROMOCHLOROM ETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1 .2 - DICHLOROETHANE
1,1,1 - TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
t,Z - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROM ETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1 ,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1 ,1,2 • TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1 ,1 ,2,2 - TETRACHLOROETHANE
o - XYLENE
1 ,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p • DICHLOROBENZENE
0 - DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1 ,3-BUTADIENE
BUND 16699
8/28/99
9/16/99
L9IN022
ppbv
0.36
0.30
0.70
0.64
ND
ND
ND
ND
ND
ND
0.31
ND
ND
0.35
0.10
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0.07
0.16
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.31
ND
ND
0.05 U
ND
ND
0.06 U
0.12
ND
0.06 U
ND
o.oa
0.03 U
0.07 U
ND
ND
ND
ND
ND
ND
BUND 16674
9/3/99
9/23/99
L31V016
ppbv
0.47
0.39
0.62
0.60
ND
ND
ND
ND
ND
ND
0.30
ND
ND
0.2B
0.10
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0.09 U
0.14
0.06 U
ND
NO
ND
NO
ND
ND
ND
ND
ND
ND
0.21
ND
ND
ND
ND
ND
0.05 U
0.09
ND
O.OS U
ND
0.06
0.05 U
0.09
ND
ND
ND
ND
ND
ND
BUND 16702
OIA/AB
079/00
9/16/99
L9IN023
ppbv
0.37
0.39
0.62
O.S7
ND
ND
ND
NO
ND
NO
0.32
NO
ND
0.27
0.10
ND
NO
ND
NR
NO
ND
ND
ND
NO
ND
D.06
0.36
0.08 U
ND
ND
ND
ND
0.44
ND
ND
NO
ND
ND
0.19
ND
ND
0.06 U
0.40
ND
0.05 U
0,10
ND
0.04 U
ND
O.OS
0.04 U
0.06 U
ND
ND
ND
NO
ND
ND
BUND terse 01
9/16/99
10/12/99
L9JK021
ppbv
0.34
0.30
0.64
0.62
ND
ND
ND
ND
ND
2.19
0.29
ND
ND
0.19
0.09
ND
ND
NO
NR
ND
ND
ND
ND
ND
ND
0.06
0.12
0.08 U
ND
ND
ND
ND
ND
ND
ND
NO
ND
ND
0.19
ND
ND
0.03 U
ND
NO
0.05 U
0.07 U
ND
0.03 U
ND
O.OS
0.04 U
O.OS U
ND
ND
ND
ND
ND
ND
U = Under Detection Limit
NO - Not Detected
E = Estimated Value
V = Voided
NA = Not Analyzed
NR = Not Reported
BUND98_C9
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Beulah, ND (BUND)
Yearly Report ( Feburary 1999 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILG
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
(fans- 1,2 - OICHLOROETHYLENE
1,1- DICHLOROETHANE
METHYL' tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1.2-DICHLOROETHYLENE
BROMOCHLOROM ETHANE
CHLOROFORM
ETHYL teft-BUTYL ETHER
1 ,2 - DICHLOROETHANE
1,1.1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
13 -D1CHLORQPRQPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYl. METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1.3 - DICHLOROPROPENE
1.1.2-TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1 ,1 ,2,2 - TETRACHLOROETH AN E
o ' XYLENE
1 ,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIMETHYLBENZENE
m • DICHLOROBENZENE
CHLOROMETHYLBENZENE
p • DICHLOROBENZENE
0- DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
BUND 16786 R1
SMS/99
10/13/99
L9JL016
ppbv
0.37
0.30
0.66
0.56
ND
ND
ND
ND
ND
2,46
0.32
ND
ND
0.21
0.10
ND
ND
NO
NR
ND
ND
ND
ND
ND
ND
0,06
0.12
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.17
ND
ND
0,03 U
ND
ND
O.OS U
0.08 U
ND
ND
ND
0,05
0.03 U
0.05 U
ND
ND
ND
ND
ND
ND
BUND 16788 02
9/16/99
10/12/99
L9JK022
ppbv
0.35
0.21
0.69
O.S4
ND
ND
ND
ND
ND
4.03
0.33
ND
ND
0.14
0.10
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0.06
0.13
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.22
ND
ND
0.05 U
ND
ND
0.05 U
0.08
ND
0.03 U
ND
0.05
0.03 U
0.04 U
ND
ND
ND
ND
ND
ND
BUND 16788 R2
8/16/99
10/13/99
L9JL017
ppbv
0.39
0.22
0.70
0.50
ND
ND
ND
ND
ND
5,37
0.36
ND
ND
0.13
0.09
ND
ND
ND
NR
ND
ND
ND
ND
ND
ND
0,05 U
0.12
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.21
ND
ND
0.04 U
ND
ND
0.05 U
0.09
ND
0.04 U
ND
0,06
0.03 U
0.05 U
ND
ND
ND
ND
ND
ND
BUND 16799
8/21/98
10/13/99
L9JL018
ppbv
0.70
0.32
0.66
O.S7
ND
ND
ND
ND
ND
ND
0.31
ND
ND
0.11
0.09
NO
NO
ND
NR
ND.
ND
ND
ND
ND
ND
0.05 U
0.16
0.10
ND
ND
ND
ND
0.02 U
ND
ND
ND
ND
ND
0.19
ND
ND
0.05 U
0.02 U
ND
0.05 U
0,10
ND
0.04 U
ND
0.06
0.03 U
0.05 U
ND
ND
ND
ND
ND
ND
U = Under Detection Umit
ND = Not Delected
E = Estimated Value
V = Voided
NA = Not Analyzed
NR = Not Reported
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Beulah, ND (BUND)
Yearly Report ( Feburary 1999 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOM ETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLGNE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1 ,2 - DICHUOROETHYLENE
1,1"- DICHLOROETHANE
METHYL teft-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1 ,2-DICHLOROETHYLENE
BRDMOCHLOROM ETHANE
CHLOROFORM
ETHYL tet^SUTYL ETHER
1 ,2 - DICHLOROETHANE
1,1,1 - TRICHLOROETH ANE
BENZENE
CARBON TETRACHLORIDE
tort-AMYL METHYL ETHER
1 ,2 - DICHLORQPROPANE
ETHYL ACRYLATE
BROM ODICHLOROM ETHANE
TRICHLOROETHYLENE
METHYL W6THACRYLATE
els -1 ,3 - DICHLOROPROPENE
METHYL JSOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1 .1,2 • TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1 ,1 ,2,2 - TETRACHLOROETHANE
o - XYLENE
1,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0- DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTAOIENE
BUND 16838 01
9/27/89
10/12/99
L9JL012
ppbv
0.54
Q.23
0.62
0.54
ND
ND
ND
NO
ND
ND
0.63
ND
ND
0.14
0.10
ND
ND
ND
NR
ND
ND
ND
ND
NO
ND
0,05 U
0.16
0.08 U
ND
ND
ND
NO
ND
NO
ND
ND
ND
ND
0.20
NO
ND
NO
ND
NO
0.05 U
0.09
ND
0.0$ U
ND
0.06
0.03 U
0.05 U
ND
ND
ND
ND
ND
ND
BUND 16838 R1
9/27/99
10/15/99
L9JN021
ppbv
0.56
0.29
0.68
0.49
ND
NO
ND
ND
ND
1.28
0.75
ND
ND
0.15
0.09
ND
ND
ND
NR
NO
ND
NO
ND
ND
ND
0.05 U
0.19
0.08 U
ND
NO
ND
ND
ND
ND
ND
NO
ND
NO
0.31
ND
ND
0.04 U
ND
ND
0.06 U
0.13
ND
0.04 U
ND
0.08
0.03 U
0.06 U
ND
ND
ND
ND
ND
ND
BUND 16840 02
9/27/99
10/13/99
L9JL013
ppbv
0.59
0.25
0.69
0.62
ND
ND
ND
ND
ND
1,51
0.33
ND
ND
0.11
0.10
ND
ND
• NO
NR
ND
ND
ND
ND
ND
ND
0.06
0.15
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.24
ND
ND
ND
ND
ND
0.05 U
0.09
ND
0.04 U
ND
0.06
0.04 U
0.05 U
ND
ND
ND
ND
ND
ND
BUND 16840 R2
9/27/99
10/16/99
L9JN022
ppbv
0.67
0.28
0.70
0.51
ND
ND
ND
ND
ND
1.44
0.35
ND
ND
0.13
0.11
ND
ND
ND
NR
ND
ND
NO
ND
ND
ND
D.06
0.20
0.08 U
ND
ND
ND
ND
ND
ND
ND
NO
ND
ND
0.39
NO
ND
0.06 U
ND
NO
0.07 U
0.14
ND
0.04 U
ND
0.09
0.03 U
0.06 V
ND
NO
ND
ND
ND
ND
U = Under Detection Limit
ND c Not Detected
E° Estimated Value
V» Voided
MA = Not Analyzed
NR = Not Reported
BUND88.98
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Brattleboro, VT (BRVT)
Yearly Report ( September 1998 - September 1999 )
SAMPtESlTE*
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CMLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADlENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METH YLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans • 1,2 - DICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,2-DICHLOROETHYLENE
BROMOCHLOROM ETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 -DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
teit-AMYL METHYL ETHER
1,2 -DICHLORQPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOflUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1 ,1.2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p - XYLENE
BROMOFORM
STYRENE
1 ,1 ,2,2 - TETRACHLOROETH ANE
o- XYLENE
1 ,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIMETH YLBENZENE
m - DICHLOROBENZENE
CHLOROM ETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
BRVT 14684
9/2/88
9/25798
L8IY01S
ppbv
1.58
0.77
0.77
0.59
ND
NO
ND
ND
ND
ND
0.36
ND
ND
ND
0.05
ND
ND
0.32
0.49
ND
ND
ND
ND
ND
ND
0.07
0.53
0.12
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.09
ND
ND
NO
ND
ND
0.20
0.50
ND
ND
ND
0.28
ND
0.18
ND
ND
ND
ND
ND
ND
BRVT 14811
3/14/98
10/19/98
L8JS020
ppbv
1.0B
0.72
0.67
0.63
ND
ND
ND
ND
ND
15,25
0.76
ND
ND
0.49
0.11
ND
ND
0.63
0.93
ND
ND
ND
ND
ND
ND
0,06
0.56
0,11
ND
ND
ND
ND
ND
ND
ND
ND
ND
NO
2.47
ND
ND
O.OB U
0.07 U
ND
0.24
0.56
ND
0.12
ND
0.27
0.06 U
0.20
ND
ND
ND
ND
ND
ND
BRVT1BOE4
9/26/88
10/22/98
LSJV010
ppbv
1.21
9.66
0.59
0.58
ND
ND
ND
ND
ND
NP
0.26
ND
ND
0,14
0.08
NO
ND
0.78
0.42
ND
ND
ND
ND
NO
ND
9.06
0.62
0.07 V
ND
ND
ND
ND
ND
ND
ND
ND
ND
NP
1.19
ND
ND
ND
0.05 U
ND
0.20
0.48
ND
0.05 U
ND
0.24
0.07 U
0.2S
ND
ND
ND
ND
ND
ND
BRVT 16113
10/8/98
10/22/98
L8JV016
ppbv
1.17
Q,75
0.57
047
ND
ND
ND
ND
ND
NO
0.27
NO
ND
0.09 U
0.09
NO
ND
0.49
0.33
ND
ND
NO
ND
ND
ND
0,06
0.66
0X18 U
ND
NO .
ND
ND
ND
ND
ND
ND
ND
ND
1.23
ND
ND
NO
0.05 U
NO
0.22
0.52
ND
0.06 U
ND
0.26
0.06 U
0.24
ND
NO
ND
ND
ND
ND
U = Under Detection Umit
ND = Not Detected
V = Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Brattleboro, VT (BRVT)
Yearly Report ( September 1998 - September 1999 )
SAMPiESlTE#
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
OICHLOROTETRAFLUOROETHANE
VjNYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITR1LE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans • 1,2 - DICHLOROETHYLENE
1,1 -DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1 ,2-DlCHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BOTYL ETHER
1 ,2 - DICHLOROETHANE
l.t.1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1 ,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1 ,1 ,2 - TRICHLOROETHANE
TOLUENE
OIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,P - XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
o - XYLENE
1,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIMETH YLBENZENE
m - DICHLOROBENZENE
CHLOROM ETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
BRVT 16137
10/20/98
12/6/98
L8LF008
ppbv
1.15
0.96
0.58
0.57
ND
ND
ND
ND
ND
ND
0.28
ND
ND
ND
0.11
ND
ND
0.22
0.49
ND
ND
ND
ND
NO
ND
0.07
0.46
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.68
ND
ND
0.06 U
ND
ND
0.14
0.34
ND
0X16 U
ND
0.20
0.08
0.22
ND
ND
ND
ND
ND
ND
BRVT 1S156
11/1/98
11/12/98
L8KK018
ppbtf
0.62
0.36
0.48
0.48
ND
ND
ND
ND
ND
ND
0.24
ND
ND
ND
0.08
ND
ND
ND
0.34
ND
ND
ND
ND
ND
ND
0.05 U
0.32
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.32
ND
ND
ND
ND
ND
0.09 U
0.17
ND
0.05 U
ND
0.11
0.05 U
0.10
ND
ND
ND
ND
ND
ND
BRVT 16196
11/13/98
12/1/98
, L8LA014
ppbv
2.39
1.10
0.62
0.61
ND
ND
0.12
ND
ND
ND
0.29
ND
ND
ND
0.12
ND
ND
0.32
0.40
ND
ND
NO
ND
ND
ND
0.09 U
0.81
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.29
ND
ND
0.07 U
ND
ND
0.26
0.68
ND
0.09 U
ND
0.33
0.12
0.30
ND
ND
ND
ND
ND
ND
BRVT1B237
11/26/98
12/8/98
L8LH013
ppbv
2.71
1.18
0.59
0.64
ND
ND
0.15
ND
ND
ND
0.27
ND
ND
0.03 U
0.27
ND
ND
0.27
0.48
ND
ND
ND
ND
ND
ND
0.06
0.83
0.11
ND
ND
ND
NO
ND
ND
ND
ND
ND
ND
1.45
ND
ND
0.07 U
ND
ND
0.26
0.67
ND
0.07 U
ND
0.36
0.11
0.30
ND
ND
ND
ND
ND
ND
U = Under Detection Limit
ND = Not Detected
V = Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Brattleboro, VT (BRVT)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITES
SAMPLE DATE
ANALYSIS PATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITR1LS
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1.1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - OICHLOROETHYLENE
1,1- DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1 ,2 - DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1 .2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROM ETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1.W- TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m.p • XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
o - XYLENE
1,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 • DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
BRVT 16261
12/7/98
12/31/98
L8LV007
ppbv
2.02
0.98
0.71
0.65
NO
ND
0.09
ND
ND
ND
0.33
ND
ND
0.27
0.11
NO
ND
O.G3
0.76
ND
ND
ND
ND
ND
ND
O.OG
0.58
0.09
ND
ND
ND
ND
ND
ND
ND
0.14
ND
ND
1.52
ND
ND
0.12
0.08 U
ND
0.20
0.4B
ND
0.09 U
ND
0.27
0.08
0.22
ND
ND
ND
ND
ND
ND
BRVT 16282
12/19/98
1/12/99
L9AK012
ppbv
4.09
1.51
0.67
0.68
ND
ND
0.18
ND
ND
0.91
0.29
0.14
ND
0.10
0.12
ND
ND
0,52
0.59
ND
ND
NO
ND
ND
ND
0.06
0.96
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
NO
1.41
ND
ND
0.09
0.06 U
ND
0.27
0.67
ND
0.09 U
ND
0.36
0.12
0.30
ND
ND
ND
ND
ND
ND
BRVT 16304
12/31/98
1/12/99
L9AK019
ppbv
3.74
1.67
0.77
0.63
ND
ND
0.18
ND
ND
2.t1
0.34
ND
ND
0,16
0.12
ND
ND
0.21
0.95
ND
ND
ND
ND
ND
ND
0.05 U
0.97
0.09
ND
ND
ND
NO
ND
ND
ND
ND
ND
ND
1.63
ND
ND
0.10
0.04 U
ND
0.26
072
ND
0.09 U
ND
0.37
0.12
0.25
ND
ND
ND
ND
ND
NO
BRVT 16318
1/12/99
1/22/99
L9AV012
ppbv
4.20
1,61
0.66
0.66
ND
ND
0.26
ND
ND
ND
0.31
NO
ND
0.44
0.11
ND
ND
0.40
0.41
NO
ND
NO
ND
ND
ND
0.05 V
1.08
0.10
ND
ND
ND
ND
ND
NO
ND
ND
ND
NO
1.72
ND
ND
0,12
ND
ND
0.32
0.87
ND
0.08 U
ND
0.43
0.13
0.36
ND
ND
ND
NO
ND
ND
U = Under Detection Unit
ND = Not Detected
V c Voided
3 o(10
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Brattleboro, VT (BRVT)
Yearly Report ( September 1998 - September 1999)
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRIL6
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans- 1,2-DICHLOROETHYLENE
1,1 -DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,2-DICHLOROETHYLENE
BROMOCHLOROM ETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 - DICHLOROETHANE
1,1.1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1.2 - DtCHLOROPROPANE
ETHYL ACRYLATE
BROMQOICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYIATE
els -1 ,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1 ,1 ,2 - TRICHLOROETHANE
TOLUENE
OIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
n),p - XYLENE
BROMOFORM
STYRENE
1,1,2,2 -TETRACHLOROETHANE
o- XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 . DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
BRVT1S349D1
1/24/89
2/2/99
L9BB011
ppbv
2.62
1.24
0.61
o.sr
NO
NO
0.18
ND
ND
5.04
0.33
ND
ND
0.06 U
0.11
ND
ND
0.34
0.52
ND
ND
ND
ND
ND
ND
0.07
0.81
0.08
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.31
ND
ND
0.11
ND
ND
0.25
0.68
ND
0.12
ND
0.3S
0.13
0.37
ND
ND
ND
ND
ND
ND
BRVT 15343 R1
1/24/99
2/9/99
L9BI007
ppbv
2.43
1,15
0.66
0.60
ND
ND
0.13
ND
ND
4.41
0.38
ND
ND
0.04 U
0.11
ND
ND
0.35
0.58
ND
ND
ND
ND
ND
ND
0.06
0.80
0.05 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.29
ND
ND
0.08 U
ND
ND
0.24
0.66
ND
0.12
ND
0.34
0.13
0.34
ND
ND
ND
ND
ND
NO
BRVT 15351 02
1/24/99
2/2/99
L9BB012
ppbv
2.73
1.30
0.62
0.61
ND
ND
0.05
NO
ND
11.19
0.33
ND
ND
0.07 U
0.09
ND
ND
0.33
0.35
ND
ND
ND
ND
ND
ND
0.05 U
0.79
0.09
ND
ND
ND
ND
ND
NP
ND
NO
ND
ND
1.25
ND
ND
0.10
ND
ND
0.24
0.63
ND
0.07 U
ND
0.33
0.12
0.31
ND
NO
ND
ND
ND
ND
BRVT1$3S1*2
1/24/99
2/9/99
L9BB008
ppbv
2.58
126
0.64
0.61
ND
ND
ND
ND
ND
13.01
0.34
ND
ND
0.05 U
0.10
ND
ND
0.32
0.41
ND
NO
NO
ND
ND
ND
0.07
0.80
0.10
ND
ND
NO
ND
ND
NO
ND
NO
ND
ND
1.20
ND
ND
0.11
ND
ND
0.23
0.61
ND
0.06
ND
0,32
0.12
0.30
ND
ND
ND
ND
ND
ND
U = Under Detection Unit
ND o Not Detected
V = Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Brattleboro, VT (BRVT)
Yearly Report (September 1998 - September 1999
SAMPtEStTE#
SAMPLE DATE
ANALYSIS DATE
PILE NAME
UNITS
ACETYLENE
PROPYLENE
OICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1 ,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - OICHLOROETH YLEKE
1,1-DICHLOROETHANE
METHYL t»rt-8BTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,2-DlCHLOROETHYLENE
BRDMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BOTYL ETHER
1,2-DICHLOROETHANE
1,1.1 -TRICHLQROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1 ,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL M6THACRYLATE
els -1.3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans • 1.3 - DICHLOROPROPENE
1 ,1 .2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p - XYIENB
BROMOFORM
STYRENE
1,1,2,2 -TETRACHLOROETHANE
0 - XYLENE
1,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIMETH YtBENZENE
m - DICHLOROBENZENE
CHLOROMBtHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHtORO-1,3-BUTADIENE
BRVT 16413
2/609
2/23/99
L9BW006
ppbv
1.24
0.61
0.63
0.65
ND
ND
0.10
ND
ND
ND
0.29
ND
ND
0.07 U
0.10
NO
ND
0.49
ND
ND
ND
ND
ND
ND
ND
0.04 U
0.46
0.07 U
ND
NO
0.09
ND
ND
0.05 t)
ND
0.27
ND
ND
0.53
ND
ND
0.05 U
ND
ND
0.14
0.29
ND
0.11
ND
0.18
0.08
0.16
0.05 U
ND
0.06 U
0.06 U
0.24
0.05 U
BRVT 15443
2/17/99
3/4/99
L9CD009
ppbv
4.07
1.71
0.59
0.67
ND
ND
0.28
ND
ND
ND
0.26
ND
ND
0.11
0.90
ND
ND
0.56
1.69
ND
ND
NO
ND
NO
ND
0.05 U
1.18
0.03 U
ND
ND
ND
ND
ND
ND
ND
0.05 U
ND
ND
2.23
ND
ND
0.11
0.09 U
ND
0.37
1.07
ND
O.OS U
ND
0,49
0.12
040
ND
ND
ND
ND
ND
ND
BRVT 15483
3/1/99
3/11/99
L9CJ019
ppbv
2.50
1.07
0.60
0.61
ND
ND
0.15
ND
ND
ND
0.34
ND
ND
ND
0.10
ND
ND
0.37
4.03
NO
ND
NO
ND
ND
ND
0.05 U
0.77
0.07 U
ND
ND
ND
ND
ND
ND
ND
0.07
ND
ND
1.11
ND
ND
0.06 V
ND
ND
0.23
0.5B
ND
0.07 U
ND
030
0.09
0.25
ND
ND
ND
ND
ND
ND
BRVt t&$47
3/13/99
3/24/99
UCX919. ,
ppbv
1.18
1.02
0.60
0.92
ND
ND
0.07
ND
ND
ND
0.37
0.89
ND
0.07 U
0.19
ND
ND
0.12
1.71
ND
ND
NO
ND
ND
ND
0.04 g
0.57
ND
ND
NO
ND
ND
ND
ND
ND
0.17
ND
ND
0.43
ND
ND
ND
ND
ND
0.12
0.26
ND
0.05 U
ND
0,16
0.05 U
0.12
ND
ND
ND
ND
ND
NO
U = Under Detection limit
NO = Not Detected
V = Voided
SollO
VI98.89
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Brattleboro, VT (BRVT)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONTTRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-OICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1,1 -DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLQROPRENE
cls-1 ,2-DICHLOROETH YLENE
BRDMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1 ,2 - DICHLOROETHANE
U.I » TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1 .2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1 ,1,2 - TRICHLOROETHANE
TOLUENE
OIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m(p-XYLENE
BROMOFORM
STYRENE
1 ,1 ,2,2 - TETRACHLOROETHANE
0 - XYLENE
1,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIMETH YLBEN2ENE
m - DICHLOROBENZENE
CMLOROMETHYLBENZENE
p • DICHLOROBENZENE
o - DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
BRVT 15687 01
3/26/89
4/43/99
L9DL01S
ppbv
1.08
0.84
0.70
0.73
ND
NO
0.07
ND
ND
NO
1.02
ND
ND
022
0.11
ND
ND
0.19
1.10
ND
ND
ND
ND
ND
ND
0.07
O.S3
0.06 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.67
ND
ND
0.05 U
ND
ND
0.15
0.38
ND
0.0$ U
ND
0.19
0.07 U
0.16
ND
ND
ND
ND
ND
ND
BRvris6$rRi
3/25/99
4/13/39
L9DM010
ppbv
1.68
0.89
0.73
0.72
ND
ND
0.07
ND
ND
ND
1.15
ND
ND
0.20
0.11
ND
ND
0.19
1.12
ND
ND
ND
ND
ND
ND
0.06
0.51
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.69
ND
ND
0.04 U
ND
ND
0.15
0.33
ND
0.04 U
ND
0.18
0.05 U
0.16
ND
ND
ND
ND
ND
NO
BRVT 15689 D2
3/26/99
4/13/99
L9DL016
ppbv
0.92
0.83
0.64
0.69
ND
ND
0.08
ND
ND
ND
0.31
ND
ND
0.13
0.11
ND
ND
0.21
1.18
ND
ND
WD
ND
ND
ND
0.06
0.56
0.04 U
ND
NO
ND
ND
ND
ND
ND
ND
ND
ND
0.72
ND
ND
0.06 U
ND
ND
0.17
0.41
ND
0.05 U
ND
0.23
0.07 U
0.17
ND
ND
ND
ND
ND
ND
BRVT 16589 R2
3/26/99
4/13/99
L9DM011
ppbv
1.89
0.81
0.67
0.67
ND
ND
0.08
ND
ND
ND
0.31
NO
ND
0.1G
0.11
ND
ND
0.22
1.17
ND
ND
ND
ND
ND
ND
0,04 U
0.58
0.04 U
ND
ND
ND
ND
ND
NO
ND
ND
ND
ND
0.72
ND
ND
0.07 U
ND
ND
0.16
0.40
ND
0.04 U
ND
0,21
0.07 U
0.14
ND
ND
ND
ND
ND
ND
U = Under Detection Limit
ND = Not Detected
V = Voided
VIB8_89
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Brattleboro, VT (BRVT)
Yearly Report (September 1998 - September 1999)
SAMPLE SITES
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROM ETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETQNITRILS
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans* 1,2-DICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tolt-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-DICHLOROETHYLENE
BROMOCHLQROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 -DICHLOROETHANE
1,1,1 -TRICMLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2-DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL M6THACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
OIBROMOCHLOROM ETHANE
1,2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m.p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
o-XYLENE
1,3,5-TRIMETHYLBENZENE
1.2,4-TRIMETHYLBENZENE
m • DICHLOROBENZENE
CHLDROMETHYLBENZENE
p- DICHLOROBENZENE
0 • DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
BRVT 16666
4/6/99
5/6/99
L9ED020
ppbv
1.34
0.69
0.66
0.62
ND
NP
0.05
ND
ND
0.92
0.35
ND
ND
0.20
0.11
ND
ND
0.26
1.40
NO
ND
ND
ND
ND
ND
0.06
0.39
0.09
ND
ND
ND
ND
ND
ND
ND
0.09
ND
ND
0.79
ND
ND
0.10
ND
ND
0.14
0.30
ND
0.05 U
ND
0.1 S
0.06 U
0.12
ND
ND
ND
ND '
ND
ND
8ftVT 15826 01
6/12/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
BRVT16828
5/12/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
BRVT tt?89
6/18/99
6/7/99
L9F0010
ppbv
0.98
0.56
0.55
0.67
0.02 U
ND
0.05
ND
ND
ND
0.29
ND
ND
0.05 U
0.12
ND
ND
0.40
0.93
ND
ND
ND
ND
ND
ND
0,07
0.34
0.08 U
ND
ND
ND
ND
ND
ND
ND
0.09
ND
ND
0.74
ND
ND
0.09
ND
ND
0.14
0.29
ND
0.08 U.
ND
0.16
0.06 U
0.14
ND
ND
ND
ND
ND
ND
U = Under Detection Limit
ND = Not Detected
V = Voided
Vt98_90
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Brattleboro, VT (BRVT)
Yearly Report (September 1998 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROM ETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans • 1,2 - DICHLOROETHYLENE
1,1 -DICHLOROETHANE
METHYLtert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1 ,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 - DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1 ,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1 ,3 - DICHLOROPROPENE
METHYL ISOflUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1 ,1 ,2 - TRICHLOROETH AN E
TOLUENE
OIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1 ,1 ,2,2 - TETRACHLOROETHANE
O.XYLENE
1 ,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIMETH YtBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 . DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
BRVT 16836
6/30/99
6/17/99
L9FQ009
ppbv
1.04
0.99
0.60
0.69
0.01 U
ND
0.06
ND
ND
ND
0.31
ND
ND
0.05 U
0.12
ND
ND
0.27
0.73
ND
ND
NO
ND
ND
ND
0.07
0.37
0.08 U
ND
ND
ND
ND
ND
ND
ND
0.12
ND
NO
0.72
ND
ND
0.14
ND
ND
0.15
0,34
ND
0.06 U
ND
0.18
0.07 U
0.1 S
ND
ND
ND
ND
ND
ND
BRVT 15838
6/5/99
6/17/99
L*TO011
ppbv
0.86
0.4B
0.55
0.62
0.01 U
ND
0.03 U
ND
ND
NO
0.29
NO
ND
0.03 U
0.11
ND
ND
0.2B
3.73
ND
ND
ND
0.03 U
ND
ND
0.06
0.29
0.09
ND
NO
ND
ND
ND
ND
ND
0.13
ND
ND
0.59
ND
ND
0.06 U
0.01 U
ND
0.11
0.24
ND
0.06 U
ND
0.13
0.06 U
0.14
ND
ND
ND
ND
ND
ND
BRVT1B9t9
6/17/99
6/29/99
L9FWOOG
ppbv
1.05
0.5B
0.64
0.64
ND
ND
0.05
ND
ND
1.97
0.58
ND
ND
0,11
0.11
ND
ND
ND
0.43
ND
ND
ND
ND
ND
ND
0.08
0.43
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
8.69
ND
ND
0.09
ND
ND
0.17
0.38
ND
0.07 0
ND
0.18
0.07 U
0.17
ND
ND
ND
ND
ND
ND
BR.VT t6022
6/29/99
7/20/99
L9GT007
ppbv
1.01
0.67
0.67
0.78
0.01 U
ND
0.05
0.02 U
ND
ND
0.33
NO
ND
0.07 U
0.10
ND
ND'
0.62
0.76
ND
ND
ND
0.02 U
ND
ND
0.07
0.43
0.09
ND
ND
ND
NO
ND
NO
ND
ND
ND
NO
0.93
ND
ND
0.09
0.02 U
NO
0.15
0.36
ND
0.07 U
ND
0.19
0.07 U
0.17
ND
ND
ND
NO
ND
ND
U « Under Detection Until
ND = Not Detected
V = Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Brattleboro, VT (BRVT)
Yearly Report (September 1998 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROP YLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
ViNYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITR1LE
TRICHLOROFLUOROMETHANE
ACRYLOMTRILE
1,1-DICHLOROETHENE
METH YLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans- 1,2 - DICHLOROETH YLENE
1,1 • DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
CIS-1.2-DICHLOROETHYLENE
BRDMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1.2 -DICHLOROETHANE
1,4,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1 .2 - D1CHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1 ,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans • 1,3 - DICHLOROPROPENE
1 ,1,2 - TRICHLOROETHANE
TOLUENE
OIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m.p-XYLENE
BROMOFORM
STYRENE.
1 ,1 ,2,2 - TETRACHLOROETHANE
o-XYLENE
1 ,3,5-TRIM ETHYLBENZENE
1 ,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLQROMETHYLBENZENE
p - DICHLOROBENZENE
g • DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
BRVt 16269
7/17/99
8/10/99
L9HJ009
ppbv
1.35
0,71
0.74
0.80
ND
ND
0.07
ND
ND
NP
0.36
NO
ND
0.08 U
0.10
ND
ND
0.30
0.93
ND
ND
ND
ND
ND
ND
0.10
0.47
0.10
ND
ND
ND
Nfi
0.09
ND
ND
ND
ND
ND
0.77
ND
ND
0.07 U
ND
ND
0.15
0,37
ND
0.06 U
ND
0.18
0.07 U
0.17
ND
ND
ND
ND
ND
ND
BRVT 16252
7/23/99
8/10/99
L9HJ008
ppbv
1.21
0.65
0.70
0.80
ND
ND
0.07
ND
ND
ND
0.32
ND
ND
O.OB U
0.10
ND
ND
0.39
1.39
ND
ND
NO
ND
NO
ND
0.07
0.43
0.12
ND
ND
ND
ND
0.02 U
ND
ND
ND
ND
NO
0.83
ND
ND
0,07 U
ND
ND
0.15
0.36
ND
0.07 V
ND
0.18
0.07 U
0.18
ND
ND
ND
ND
ND
ND
BRVT 16283
8/4/99
8/16/99
LPHP011
ppbv
0.76
0.47
0.71
0.64
ND
ND
ND
ND
ND
ND
0.40
ND
ND
0.05 U
0.10
ND
ND
0.35
0.59
ND
ND
ND
ND
ND
ND
0.06
0.33
0.09
ND
ND
NO
NO
ND
ND
ND
ND
ND
ND
0.67
ND
ND
0.06 U
0.01 U
ND
0.11
0.24
ND
0.05 U
ND
0.13
0.06 U
0.13
ND
ND
ND
ND
ND
ND
BRVT 16496
8/16/99
9/3/99
L9IB016
ppbv
0.74
0.42
0.60
0.60
ND
N° .. .. .;•
0.04 U
NO
NO
NO
0.30
ND
ND
0.03 V
0.10
ND
ND
0.20
1.41
ND
NO
NO
ND
NO
ND
0.05 U
0.33
0X19
ND
ND
ND
ND
ND
NO
ND
NO
ND
ND
0.51
ND
ND
0.05 U
ND
ND
0.14
0.23
ND
0.14
ND
0.12
0.05 U
0.12
ND
ND
ND
ND
ND
NO
U c Under Detection Limit
NO = Not Detected
V = Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Brattleboro, VT (BRVT)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-DICHLOROETHYLENE
BROMOCHUOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1 ,2 - DICHLOROETHANE
1,1,1 - TRICHUOROETHANH
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1 ,2 - DICHLOROPROPANE
ETHYL ACRYLATE
8ROMOD1CHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1 ,1 ,2 - TRICHLOROETHANE
TOLUENE
OIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYtENE
BROMOFORM
STYRENE
1.1 ,2,2 - TETRACHLOROETHANE
o-XYLENE
1 ,3,5-TRIM ETHYLBENZENE
1A4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHt-OROMETHYLBENZENE
p - DICHLOROBENZENE
0 • OICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORQ-1.3-BUTADIENE
BRVT 16611
8/28/89
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
BRVT t66t3
3/3/99
9/14/99
L9IN014
ppbv
1.30
0,57
0.68
0.70
ND
NO
0.09
ND
ND
ND
0.33
ND
ND
ND
0.10
ND
ND
0.21
0.38
ND
ND
NO
0.06
ND
ND
0.06
0.47
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.83
ND
ND
0.07 U
ND
ND
0.16
0.37
ND
0.06 U
ND
0.19
0.08
0.19
ND
ND
ND
ND
ND
ND
BRVT 16803
9/9/99
10/6/99
L9JF008
ppbv
0.58
0.67
0.66
o.rs
ND
ND
0.06
ND
ND
ND
0.38
0.35
ND
0,14
0.12
ND
ND
0.71
0.53
ND
ND
ND
ND
ND
ND
0.06
0.54
0.11
0.06
ND
ND
ND
0.02 U
ND
ND
ND
ND
ND
1.14
ND
ND
0.07 U
0.05 U
ND
0.18
0.42
ND
0.07 U
ND
0.22
0.08
0.20
ND
ND
ND
ND
ND
ND
BRVT 16903
9/21/99
10/11/99
L9JK008
ppbv
0.38
0.74
1.60
0.70
ND
NO
0.07
ND
ND
ND
0.30
0.31
ND
ND
0.11
ND
ND
0.27
0.36
NO
ND
ND
ND
ND
ND
0.06
0.45
0.10
ND
NO
ND
ND
ND
ND
ND
ND
ND
ND
0.81
ND
ND
0,07 U
ND
ND
0.14
0.36
ND
0.06 U
ND
0.19
0.07 U
0.18
ND
NO
ND
ND
ND
ND
U = Under Detection Umll
NO = Not Detected
V n Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Burlington, VT (BUVT)
Yearly Report (September 1998 - September 1999 )
SAMPLE SITE #
SAMPtEDATE
ANALYSIS DATS
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROM ETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BRQMOMEWANE
CHLOROETHANE
ACETONITRIUE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans- 1,2 • DICHLOROETHYLENE
1,1 -DICHLOROETHANE
METHYL t«rt-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1 ,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 -DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLORQMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1 ,3 - DICHLOROPROPENE
WETHYMSQBUTYL KETONfc
trans - 1.3 • DICHLOROPROPENE
1,1,2 - TRICHLQROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1 ,1 ,2,2 - TETRACHLOROETH ANE
0 - XYLENE
1 ,3,5-TRIMETHYLBENZENE
1 ,2,4-TRlMETH YLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBEN2ENE
p - DICHLOROBENZENE
o - DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADiENE
BUVTt4677
912133
$/2S/98
L81Y017
ppbv
2.30
1.27
0.84
0.77
ND
ND
0.11
ND
ND
ND
0.39
ND
ND
ND
0.07
ND
ND
0.47
0.53
NP
ND
ND
ND
ND
ND
0.07
0.92
o.«
ND
ND
ND
ND
ND
HO
ND
NP
ND
ND
2.24
ND
ND
0.36
ND
ND
0.33
0.91
ND
ND
ND
0.50
ND
0.29
ND
ND
ND
ND
ND
ND
BUVT 14818
9/14/9$
10/14/98
L8JM011
ppbv
2.73
1.43
0.64
0.54
ND
ND
0.22
NP
ND
ND
0.30
ND
ND
0.16
0.09
ND
ND
0.48
0.36
ND
ND
ND
0.04
ND
ND
0.08
1.07
0.10
ND
ND
ND
ND
ND
ND
ND
NO
ND
ND
2.60
ND
ND
0.10
0.02 U
ND
0.3S
1.00
ND
0.12
ND
0.50
0.15
0,45
ND
ND
ND
ND
ND
ND
BUVT 15083
9«6/98
10/22/38
L8JV003
ppbv
1.66
0.96
0.53
0.45
ND
ND
0.13
NO
ND
ND
0.24
ND
ND
0.04 U
0.08
ND
ND
0.62
0.53
ND
ND
ND
ND
ND
ND
0.05 U
0.91
0.09
ND
ND
ND
ND
ND
NO
ND
NP
ND
ND
1.74
ND
ND
0.04 U
ND
ND
0.30
0.81
ND
0.07 U
ND
OM
0.10
0.34
ND
ND
ND
ND
ND
ND
BUVT«t07
10W8
10/22798
L8JV019
ppbv
2.15
1.44
0.55
0.44
ND
ND
0.18
NP
ND
ND
0.25
ND
ND
0,19
0.07
ND
ND
0.54
0.25
ND
ND
ND
ND
ND
ND
0.0$
1.33
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.25
NP
ND
0.05 U
ND
ND
0.40
1.19
ND
0.10 U
ND
0.58
0.14
0.51
ND
NO
ND
ND
ND
ND
U = Under Detection Limit
ND ° Not Detected
V * Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Burlington, VT (BUVT)
Yearly Report ( September 1998 • September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETON1TRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLEHE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans • 1.2 • DICHLOROETHYLENE
1,1 -DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 -DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2- DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROM ETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1 ,3 - DICHLOROPROPENE
1 ,4,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROM ETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p - XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
0- XYLENE
1,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIMETH YLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p • DICHLOROBENZENE
o • DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLDRO-1,3-BUTADIENE
BU\fT 16147
10/16/98
16/30/98
L8J%009
ppbv
2.10
1.22
0.57
0.52
ND
ND
0.08
ND
ND
ND
0.25
ND
ND
ND
0.08
ND
ND
0.26
0.38
NO
ND
ND
ND
ND
ND
0.05 U
0.74
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.45
ND
ND
0.04 U
ND
ND
0.24
0.74
ND
0,05 U
ND
0.36
0.12
0.40
ND
ND
ND
ND
ND
ND
BUVT 15153
11/1/98
11/12/98
L8KK017
ppbv
2.36
1.22
0.73
0,56
ND
ND
0.13
ND
ND
ND
0.51
ND
ND
0.17
0.08
ND
ND
0.1 5
0.46
ND
ND
ND
ND
ND
ND
0.06
0.86
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.73
ND
ND
0.07 U
ND
ND
0.30
0.80
ND
0.11
ND
0.39
0.14
0.37
ND
ND
ND
ND
ND
ND
BUVT 151 97
11/13/98
12/1/98
L8LA013
ppbv
3.77
1.80
0.63
0.57
ND
ND
0.28
ND
ND
ND
0.29
ND
ND
0.08 U
0.08
ND
ND
0.30
0.23
ND
ND
ND
ND
ND
ND
0.07
1.29
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.41
ND
ND
0.09
ND
ND
0.38
1.10
ND
0.12
ND
0.55
0.18
0.52
ND
ND
ND
ND
ND
ND
BUVT 15235
11/26/9$
12/8/98
L8LH012
PPPV
2.33
1.08
0.63
0,58
ND
ND
0.17
NO
ND
ND
0.31
ND
0.10
0.09 U
ND
ND
ND
0.18
0.31
ND
ND
ND
ND
ND
ND
0.07
0.83
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.68
ND
ND
0.03 U
ND
ND
0.27
0.71
ND
0.10 U
ND
0.36
0.12
0.34
ND
ND
ND
ND
ND
ND
U = Under Detection Until
NO ° Not Detected
V = Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Burlington, VT (BUVT)
Yearly Report (September 1998 - September 1999 )
SAMPLE SITE # .
SAMW.60ATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMEIHANE
DICHLOROTETRAFLUOROHTHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1 ,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans- 1.2 - PICHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
CIS-1.2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-eUTYL ETHER
1,2 - DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
U-DICHLOROPROPANE
ETHYL ACRYLATE
BROMOD1CHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL 1SOBUTYL KETONE
trans • 1 ,3 - DICHLOROPROPENE
1 .1 ,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
ttl,p - XYLENE
BROMOFORM
STYRENE
1 .1 ,2,2 - TETRACHLOROETHANE
0 - XYLENE
1,3,5-TRIMETHYLBENZENE
1 ,2,4-TRlMETH Y4.BENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
o-DIOHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
BUVT 16249
12/7/98
12/31/98
L8LV006
ppbv
2.32
1.20
0.63
0.63
NO
ND
0.13
ND
ND
5.25
0.34
0.27
ND
0.30
0.11
ND
ND
049
0.30
ND
ND
ND
ND
ND
ND
0X17
0.88
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.98
ND
ND
0.11
ND
ND
0.34
0.99
ND
0.09 U
ND
0.48
0.16
0.45
ND
ND
ND
ND
ND
ND
BUVT 15284
12/19/98
1/11/99
L3AK011
ppbv
3.63
1.23
0.72
0.60
ND
ND
0.16
ND
ND
1.16
O.SO
ND
ND
0.11
0.08
ND
ND
0.16
0.35
ND
ND
ND
ND
ND
ND
0.05 U
0.81
0.07 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.49
ND
ND
0.07 U
ND
ND
0.25
0.60
ND
0.10
ND
0.33
0.10
048
ND
ND
ND
ND
ND
ND
BUVT f 5310
12/31/98
1/12/99
L9AK020
ppbv
5.16
1.66
0.69
0.63
ND
ND
0.22
ND
ND
ND
0.29
ND
ND
0.54
0.08
ND
ND
0.11
0.09
ND
ND
ND
ND
ND
ND
0.05 U
1.16
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.05
ND
ND
0.12
ND
ND
0.40
1.07
ND
0,07 U
ND
0.69
0.12
0.32
ND
ND
ND
ND
ND
NO
BUVT 16326 .
1/12/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V . ..-.
V
V
V
V .
u = Under Detection Limit
ND = Not Delected
V* Voided
Vt98_B9
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Burlington, VT (BUVT)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1.1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1,1 • DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1 ,2-DICHLOROETH YLENE
BROMOCHLOROMETHANE
CHLOROFORM
EW YL tert-BOTYU ETHER
1,2 -DICHLOROETHANE
1,1.t -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
\.t~ DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1 ,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p - XYLENE
BROMOFORM
STYRENE
1 .1 ,2,2 - TETRACHLOROETHANE
0 • XYLENE
1 ,3,5-TRIMETHYLBENZENE
1 ,2,4-TRlMETHYLBENZENE
m - DICHLOROBENZENE
CHLORQMETHYLBENZENE
p - DICHLOROBENZENE
o - DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
BUVT 15354 01
1/24/99
2/2139
L9BB013
ppbv
2.57
1.16
0.64
0.68
ND
ND
0.13
ND
ND
ND
0.30
ND
ND
0.05 U
0.09
ND
ND
0.29
0.16
ND
ND
ND
ND
ND
ND
0.06
0.73
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.37
ND
ND
0.07 U
ND
ND
0.27
0.74
ND
O.OB U
ND
0.38
0.13
0.34
ND
ND
ND
ND
ND
ND
BUVT 15364 R1
1/24/99
2/9/99
L9BB009
ppbv
2.27
1.13
0.64
0.61
ND
ND
0.16
ND
ND
ND
0.26
ND
ND
0.08 U
0.05
ND
ND
0.30
0.16
ND
ND
NO
ND
ND
ND
0.04 U
0.74
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.33
ND
ND
0.07 U
ND
ND
0.26
0.72
ND
O.fO U
ND
0.37
0.13
0,35
ND
ND
ND
ND
ND
ND
BUVT 1S3S6 02
1/24/99
2/3/99
L9BB014
ppbv
2.51
1.13
0.64
0.62
ND
ND
0.19
ND
ND
NO
0.30
ND
ND
0.08 U
0.08
ND
ND
041
0.30
ND
ND
ND
ND
ND
ND
046
0.76
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.38
ND
ND
0.07 U
ND
ND
0.29
0.77
ND
0.09 U
ND
0.38
0.13
0.36
ND
ND
ND
ND
ND
ND
BUVT 15356 R2
1/24/99
2/9/99
L9BB010
ppbv
2.36
1.05
0.63
0.66
ND
ND
0.16
ND
ND
0.78
0.33
ND
ND
0.07 U
0.09
ND
ND
0.29
0.43
ND
0.10
ND
ND
ND
ND
0.06
0.74
0,07 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.37
ND
ND
0.09
ND
ND
0.26
0.73
ND
0.10 U
ND
0.37
0.14
0,36
ND
NO
ND
ND
ND
ND
U = Under Detection Limit
ND = Not Detected
V = Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Burlington, VT (BUVT)
Yearly Report (September 1998 - September 1999 )
SAMPLE SITE #
SAMPtEDATE
ANALYSIS DAtE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLQNITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans- 1,2 - DICHLOROETHYLENE
1,1 -DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1 ,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1.2- DICHLOROETHANE
1,1,1 - TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2-DICHLOROPROPANE
ETHYL ACRYLATE
BROMOD1CHLOROMETWANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL 1SOBUTYL KETONE
trans - 1 ,3 • DICHLOROPROPENE
1,1,2- TRICHLOROETHANE
TOLUENE
PIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLQROBENZENE
ETHYLBENZENE
m,p - XYLENE
BROMOFORM
STYRENE
1,1,2,2 -TETRACHLOROETHANE
0- XYLENE
1 ,3,5-TRIMETHYLBENZENE
1 ,2.4-TRIMETH YLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 • DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLDRO-1,3-BUTADIENE
BUVT 16405
2/S/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
BUVT 15449
2/17799
3/4/99
L9CD013
ppbv
1.78
132
0.62
0.60
NO
ND
ND
0.17
ND
ND
0.53
ND
ND
0.19
0.09
ND
ND
0.22
0.59
ND
ND
ND
ND
ND
ND
0.06
1.01
ND
ND
NO
ND
ND
ND
ND
ND
ND
ND
ND
1.61
NO
ND
0.06 U
ND
ND
0.28
0.83
ND
0.05 U
ND
0.40
0.10
0.33
ND
ND
ND
NO
ND
ND
BUVT tS477
2/23/99
3/10/99
L9CJ017
ppbv
3.24
1.23
0.62
0.69
ND
ND
0.17
ND
ND
ND
0.30
ND
ND
0.11
0.09
ND
ND
ND
0.25
ND
ND
ND
ND
ND
ND
0.05 U
1.00
0.07 V
ND
ND
ND
ND
ND
ND
ND
•NO
ND
ND
1.37
ND
ND
0X16 U
ND
NO
0.25
0.75
ND
0.05 U
ND
0.35
0.08
0.18
ND
ND
ND
ND
ND
ND
BUVT 15481
3/1/99
3/11/99
L9CJ018
ppbv
5.04
1.98
0.65
0.67
ND
ND
0.29
ND
ND
ND
0.37
ND
ND
0.13
0.09
ND
ND
0.41
3.71
ND
ND
ND
ND
ND
ND
0.05 U
1.31
0,08 V
ND
ND
ND
ND
ND
ND
ND
0,12
ND
ND
2.30
ND
ND
0.09
ND
ND
0.43
1.34
ND
0.11
ND
0.65
0.19
0.59
ND
ND
ND
ND
ND
ND
U = Under Detection Unit
ND » Not Detected
V - Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Burlington, VT (BUVT)
Yearly Report ( September 1998 - September 1999 )
AMPLE SITE #
AMPLE DATE
NAUYSIS DATE
ILENAME .
NITS
CETYLENE
ROPYLENE
ICHLORODIFLUOROMETHANE
HLOROMETHANE
ICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
3-BUTADIENE
ROMOMETHANE
HLOROETHANE
CETONITRiLE
RICHLOROFLUOROMETHANE
CRYLONITR1LE
1-DICHLOROETHENE
ETHYLENE CHLORIDE
RICHLOROTRIFLUOROETHANE
rans- 1,2 ' DICHLOROETHYLENE
,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
HLOROPRENE
is-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYU ETHER
,2 -DICHLOROETHANE
,1,1 • TRICHLOROETHANE
BENZENE
CARSON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2- DICHLOROPROPANE
ETHYL ACRYLATE
BROMOOICHLDROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1,3 - OICHLOROPROPENE
METHYL 1SOBUTYL KETONE
trans • 1,3 - DICHLOROPROPENE
1,1,2 -TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROM ETHANE
1,2-OIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1 ,1,2,2 - TETRACHLOROETHANE
0 - XYLENE
1 .3,5-TRIMETHYLBENZENE
1 A4-TR1METHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
o • DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
BUVT1SSS3
3/13/99
3/24/99
L9CX014
ppbv
2.06
0.88
0.90
0.62
ND
ND
0.12
ND
ND
ND
0.36
ND
ND
ND
0.08
ND
ND
0.28
0.46
ND
ND
ND
ND
ND
ND
0.06
0.67
O.OS U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.96
ND
ND
0.05 U
ND
ND
0.21
0.5S
ND
0.03 U
ND
0.30
0.08
0.21
ND
ND
ND
ND
ND
ND
BUVT 15602 01
3/25/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
BUVT 16604 O2
3/25/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
, V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
BUVT 15644
4/6/99
4/22/99
L8DV007
ppbv
2.60
1.17
0.65
0.68
ND
ND
0.14
ND
ND
ND
0.31
ND
ND
0.18
0.10
NO
ND
0.29
1.25
ND
ND
ND
ND
ND
ND
0.06
0.77
0.09 U
ND
NO
ND
ND
ND
ND
ND
0,07
ND
ND
2.81
NO
ND
0.08 U
0.03 U
ND
0.29
0.80
ND
0.09 U
ND
0.39
0.11
0.31
ND
ND
ND
ND
ND
ND
U = Under Detection Umll
ND = Not Detected
V = Voided
VtBB_98
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Burlington, VT (BUVT)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITE*
$AMPtE0ATE
ANALYSIS DAtE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMSTHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1.1-OICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans- 1.2 - DICHLORQETHYLENE
1,1 -DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1 ,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 - DICHLOROETHANE
1,1,1 -TRtCHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1 ,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMOD1CHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1 ,3 - DICHLOROPROPENE
METHYL ISOBUTYt KETONE
trans - 1,3 - DICHLOROPROPENE
1 it ,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLORPBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 -TETRACHLOROETHANE
0 • XYLENE
1,3,5-TRIMETHYLBENZENE
1 &4-TRIMETH YtBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
o. DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLDRO-1.3-BUTADIENE
BUVT 16676
4/18/99
5/11/99
L9EJ013
ppbv
2.30
1.22
0.69
0.68
ND
ND
0.16
ND
ND
ND
0.32
NO
ND
0.06 U
0.09
NO
ND
0.44
0.66
NO
ND
ND
0.01 U
ND
ND
0.08
0.77
0.07 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.40
NO
ND
0X19
ND
NO
0.28
0.77
ND
0.07 U
ND
0.39
0.13
0.33
ND
ND
ND
ND
ND
ND
BUVT 16733
4/30/99
6/18/99
L9RR012
ppbv
3.55
1.93
0.78
0.75
ND
ND
0.26
ND
ND
ND
0.33
ND
ND
0.69
0.09
NO
ND
0.49
0.81
ND
ND
ND
ND
ND
ND
Q.07
1.30
0,08
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.43
NO
ND
0.11
0.07 U
ND
0.47
1.30
ND
0.10 U
ND
0.67
0.19
0.49
ND
ND
ND
ND
ND
ND
SUVT 15795 O1
6/12/99
917199
L9FG005
ppbv
1.94
1.02
0.59
0.66
0.02 U
ND
0.15
ND
ND
ND
0.32
ND
ND
0.17
0.09
ND
ND
0.21
0.66
ND
ND
ND
ND
ND
ND
0.08
0.63
0.06 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
NO
1.20
NO
ND '
0.09
0.02 U
NO
0.23
0.60
ND
0,06 U
ND
041
0.09
0.25
ND
ND
ND
ND
ND
ND
BUVT 15795 R1
6/12/99
6/9/99
L9FI006
ppbv
2.04
0.96
0.62
0,67
0.02 U
ND
0.14
ND
ND
ND
0.68
ND
ND
0.18
0.09
ND
ND
022
0.70
NO
ND
ND
ND
ND
ND
0.06
0.62
0,06 U
ND
ND
ND
NO
ND
ND
NO
ND
ND
ND
1.18
NO
ND
0.09
ND
ND
0.25
0.64
ND
0.10 U
ND
0.34
0.12
0.29
ND
ND
ND
ND
ND
ND
U = Under Detection Limit
ND = Not Detected
V = Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Burlington, VT (BUVT)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROM ETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BRDMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRJLE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL tert-BOTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1 ,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2-DICHLOROETHANE
M.1 - TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2- DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL. METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYt 1SOBUTYL KETONE
trans - 1.3 - DICHLOROPROPENE
1 ,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p • XYLENE
BROMOFORM
STYRENE
1 ,1 ,2,2 - TETRACHLOROETHANE
0 • XYLENE
1,3,5-TRIMETHYLBENZENE
1 ,2,4-TRlMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
o • DICHLORQBENZENE
1.2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTAD|ENE
8UVT1S797O2
5/12/99
6/7/99
L9FQ006
ppbv
1.99
0.99
0.61
0.62
0.03 U
ND
0.13
ND
ND
ND
0.37
NP
ND
0.16
0.11
ND
ND
0.23
0.50
ND
ND
ND
ND
ND
ND
0418
0.65
0.10
ND
ND
ND
ND
ND
ND
ND
NP
ND
ND
1.23
ND
ND
0.11
0.02 U
ND
0.26
0.96
ND
0.09 U
ND
O.M
0.12
0.27
ND
ND
ND
ND
ND
ND
BUVT 15787 R2
5/1J/99
6/9/99
L9FI006
ppbv
1.89
0.86
0.59
0.60
0.03 U
ND
0.12
NO
0.03 U
ND
0.81
ND
ND
0.17
0.09
NP
ND
021
0.38
ND
ND
ND
ND
ND
ND
0.07
0.61
0.09
ND
ND
ND
NP
ND
ND
ND
ND
ND
ND
1.14
ND
ND
0.10
0.02 U
ND
0.25
0.63
ND
0.10 U
ND
0.32
0.13
0*7
ND
ND
ND
ND
0.02 U
0.01 U
BUVT 16793
6/24/99
6/7/99
L9FG013
ppbv
1.96
0.83
0.59
0.68
0.02 U
ND
0.10
0.03 U
0.06 U
0.97
0.29
ND
ND
0.08 U
0.10
ND
ND
0.38
0.46
NP
ND
ND
0.03 U
ND
ND
04)7
0.53
0.10
ND
ND
ND
NO
ND
ND
ND
0.10
ND
ND
1.09
ND
ND
o.«
0.02 U
NP
0.22
0.50
ND
0.09 U
ND
0.26
0.10
0.29
ND
ND
ND
NP
ND
ND
BUVT 16840
6/5/99
6/17/99
L9FQ012
ppbv
1.46
0.80
0.56
0.70
0.01 U
ND
0.11
0.02 U
ND
ND
0.27
ND
ND
0.07 U
0.09
ND
ND
026
0.64
ND
ND
ND
0.02 U
ND
ND
0.06
0.51
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.18
ND
ND
0.11
0.02 U
ND
0.23
0.67
ND
0.08 U
ND
0.29
0.10
0,26
ND
ND
ND
ND
ND
ND
U = Under Detection Unit
ND = Not Detected
V = Voided
V\9a_99
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Burlington, VT (BUVT)
Yearly Report (September 1998 - September 1999 )
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATS
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMQMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRItE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans* 1.2 - DICHLOROETHYLENE
1,1 -DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1 ,2 • DICHLOROETHANE
1,1,1 - TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1 ,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMOOICHLQROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1,3 - DICHLOROPROPENE
METHYL 1SOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 -TRICHLOROETHANE
TOLUENE
PIBROMOCHLDROMETHANE
1,2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p - XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
0 - XYLENE
1 ,3,5-TRIMETHYLBENZENE
1 ,2.4-TRlMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
o - DICHUOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
BUVT 15921
6/17/99
6/29/93
L9RWJ08
ppbv
1.63
0.94
0.56
0.63
0.01 U
NO
0.13
ND
ND
ND
0.51
NO
ND
025
0.09
ND
ND
0.39
0.54
ND
ND
ND
0.02 U
ND
ND
OAT
0.65
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.62
ND
ND
0.09
ND
ND
0.27
0.72
ND
0.09 U
ND
043
0.11
0.26
ND
ND
ND
NP
ND
ND
BUVT 16024
6/29/99
7/20/99
LPGT006
ppbv
1.72
1.0S
0.68
0.72
ND
ND
0.14
ND
ND
17.34
0.34
ND
ND
0.08 U
0.10
' ND
ND
0.47
0.53
ND
ND
ND
ND
ND
ND
0.07
0.71
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.95
ND
ND
0.12
0.02 U
ND
0.27
0.68
ND
0.11
ND
0.36
0.11
0.31
ND
ND
0.02 U
ND
ND
ND
BUVT 16260
7/17/99
8/10/99
L9HJ007
ppbv
2.13
1.19
0.84
0.85
ND
ND
0.14
0.03 U
ND
ND
0.38
ND
ND
1.68
0.11
ND
ND
040
2.86
NO
ND
ND
ND
ND
NO
0.08
0.93
0.10
ND
ND
ND
ND
0.03 U
ND
ND
0.26
ND
ND
4.23
NO
ND
0.15
0.02 U
NO
0.52
1.15
ND
0.23
ND
0£5
0.15
0.43
ND
ND
ND
ND
ND
NO
BUVT 16262
7/39/9$
8/10/39
L9HJ014
ppbv
2.60
1.43
0.79
0.80
ND
NO
0.20
ND
ND
ND
0.37
ND
ND
0.16
0.11
NO
ND
0.37
0.48
NO
ND
ND
ND
NO
ND
0.06
0.87
0.11
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.72
NO
ND
0.11
ND
NO
0.33
046
NO
0.09 U
ND
0.40
0.13
0,35
NO
ND
ND
ND
ND
ND
U - Under Detection Unit
ND = Not Detected
V - Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) • Burlington, VT (BUVT)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRJLE
1.1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans • 1,2 - DICHLOROETHYLENE
1,1 - DICHLOROETH ANE
METHYL eert-BOTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1 ,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL «ert-BUTYL ETHER
1 ,2 - DICHLOROETHANE
4,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1 ,2 • DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1 ,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1 ,1 ,2 - TRICWLOROETHAN E
TOLUENE
DIBROMOGHLOROMETHANE
1,2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1 ,1 ,2,2 - TETRACHLOROETH ANE
0 • XYLENE
1,3,5-TRIMETHYLBENZENE
1 ,2,4-TRlMETH YIBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
o - DICHUOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACMLORO-1,3-BUTADIENE
BUVT 16277
8/4/99
8/16/99
L9HP010
ppbv
2.15
1.22
0.73
0.74
ND
ND
0.16
ND
ND
ND
0.43
ND
ND
0.07 U
0.10
ND
ND
0.24
O.S1
ND
ND
ND
0.02 U
ND
ND
0.07
0.74
0.12
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.42
ND
ND
0,11
0.03 U
ND
0.27
0.76
ND
0.09 U
ND
0.37
0.11
0.30
ND
ND
ND
ND
ND
ND
BUVT 16494
8/16/99
9/3/99
U9IB01S
ppbv
1.84
1.03
0.68
0.66
ND
ND
0.13
NO
ND
NO
0.90
ND
ND
0.22
0.09
ND
ND
0.67
0.26
ND
ND
ND
0.04 U
ND
ND
0.06
0.72
0.09
ND
ND
ND
ND
ND
NO
ND
ND
ND
ND
1.38
NO
ND
0.08 U
ND
ND
0.2S
0.63
ND
0.08 U
ND
0.30
0.10
0.26
ND
ND
ND
ND
ND
ND
BUVT 16616
8/28/99
9/14/99
L9IN013
ppbv
1.55
1.10
0.56
0.65
ND
ND
0.12
ND
ND
NO
0.30
ND
ND
0.18
0.08
ND
ND
0.69
0.43
ND
ND
ND
0.04 U
ND
ND
0.05 U
0.74
D.08 U
ND
ND
ND
ND
0.02 U
ND
ND
ND
ND
ND
2.84
ND
ND
0.10
0.03 U
ND
0.47
1.05
ND
0.16
ND
0.47
0.10
0.27
ND
ND
ND
ND
ND
ND
BUVT 16805
9/9/99
10/6/99
L9JF009
ppbv
0.62
0.93
0.67
0.62
ND
ND
0.12
ND
ND
ND
0.34
, 0.21
ND
0.09 U
0.14
ND
ND
0.42
0.46
ND
ND
ND
ND
ND
ND
0.07
0.69
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.37
ND
ND
0.11
ND
ND
0.27
0.70
ND
0.08 U
ND
0.33
0.10
0,28
ND
ND
ND
ND
ND
ND
U = Under Detection Umit
ND = Not Detected
V = Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Burlington, VT (BUVT)
Yearly Report ( September 1998 - September 1999 )
U = Under Detection Limit
NO = Not Deluded
V = Voided
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - t,2 - DICHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL tett-BUTYL ETHER
M ETHYL ETHYL KETONE
CHLOROPRENE
cis-1 ,2-DICHLOROETH YLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 - DICHLOROETHANE
1,1,1-TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1 ,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1 ,1 ,2 - TRICHLOROETHANE
TOLUENE
DIBROMQCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
0 • X YLENE
1,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIM ETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p-OICHLOROBENZENE
o • DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
BUVT 16901
9#1«$
10/14/99
L9JN006
ppbv
0.58
1.14
0.67
0,55
ND
ND
0.17
ND
ND
ND
0.36
0.22
ND
0.09 U
0.12
ND
ND
020
0.89
NO
ND
ND
ND
ND
ND
0.07
0.65
0,10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.38
ND
ND
0.08 U
ND
ND
0.27
0.73
ND
0.10 U
ND
0.35
0.12
0,30
ND
ND
ND
ND
ND
ND
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Camden, NJ (CANJ)
Yearly Report (September 1998 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-OICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans • 1,2 • DICHLOROETHYLENE
1,1 - OICHLOROETHANE
METHYL tert-eUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-U-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 - DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIOE
tcrt-AMYL METHYL ETHER
1,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLQROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1,3 • DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 • TRICHLOROETHANE
TOLUENE
DI8ROMOCHLDROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4VrRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
o, DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
CANJ 14769
9/8/98
9/25/98
L8IY020
ppbV
0.63
0.25
0.83
0.52
ND
ND
ND
ND
ND
ND
0.35
ND
ND
ND
0.07
ND
ND
0.68
1.14
ND
ND
ND
ND
ND
ND
0.06
0.38
0.11
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.61
ND
ND
0.36
ND
ND
0.10
0.28
ND
ND
ND
0.16
ND
0.09
ND
ND
ND
ND
ND
ND
CANJ 14889
9/14/98
10/14/98
L8JM013
ppbtf
1.18
0,68
0.60
0.86
ND
ND
ND
ND
ND
NO
0.29
0.96
ND
0.13
0.08
ND
ND
0.70
0.67
ND
ND
ND
ND
ND
ND
0.07
045
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.69
ND
ND
0.08 U
ND
ND
0.13
0.31
ND
0.06 U
ND
0.16
0.09
0.20
ND
ND
0.05 U
ND
ND
NO
CANJ 14969
9/20/98
10/14/98
L8JM027
ppbv
140
1.«8
0.76
0.85
ND
ND
0.04 U
ND
ND
ND
0.28
1.0D
ND
0.17
0.09
ND
ND
1.66
0.78
ND
ND
ND
ND
ND
ND
0,10
0.75
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.67
ND
ND
0.06 U
0.05 U
ND
0.23
0.64
ND
0.07 0
ND
0.30
0.08
0.27
ND
ND
0.09
ND
ND
ND
CANJ 15085
10/2/98
10/22/98
L8JV018
ppbv
1.44
1.19
0.66
0.82
ND
ND
ND
ND
ND
ND
0.29
0.64
ND
0.13
0.07
ND
ND
1.26
0.77
ND
ND
ND
ND
ND
ND
0.07
0.93
0.07 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.25
ND
ND
0.10
0.07 U
ND
0.20
O.S8
ND
0.06 U
ND
0.28
0.08
0.26
ND
ND
0.10
ND
ND
ND
U = Under Detection Limit
ND = Not Detected
V = Voided
CANJ98J9
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Camden, NJ (CANJ)
Yearly Report ( September 1998 - September 1999)
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans • 1,Z -DICHLOROETHYLENE
1,1 • DICHLOROETHANE
METHYL fcffcSUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,2-OICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tort-BUm ETHER
14 • DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
12 - OICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL 1SOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
V-OIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 -TETRACHLOROETHANE
O'XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1,24-TRICHLOROBENZENE
HEXACHLORO-1 ^-BUTADIENE
CANJ 16120
10/14/98
10/30/98
Lw%oor
ppbv
1.62
0.96
0.70
0.71
ND
ND
ND
ND
ND
ND
0.39
ND
ND
0.18
0.08
ND
ND
0.71
0.90
ND
ND
ND
ND
ND
ND
0.07
0.61
9J09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.04
ND
ND
024
0.11
ND
0.16
040
ND
ND
ND
0.18
0.07 U
0.17
ND
ND
0.06 U
ND
ND
ND
CANJ 15143
10/26/98
11/3/98
L8KC013
ppbV
3.64
1.56
0.91
0.89
ND
ND
0.13
ND
ND
ND
0.37
1.0S
ND
0.40
0.09
ND
ND
20.2
0.82
ND
ND
ND
ND
ND
ND
0.17
0.82
0.10
ND
ND
ND
NO
0.06 U
ND
ND
ND
ND
ND
1.94
ND
ND
0.13
0.09 U
ND
0.26
0.76
ND
0.16
ND
0.37
0.13
0.38
ND
ND
0.11
ND
ND
ND
CANJ 15177
11/W98
11/18/98
L8KR011
ppbv
1.88
0.77
0.51
0,53
ND
ND
0.07
0.12
ND
0.72
0.26
ND
ND
0.06 U
0.07
ND
ND
0.59
0.45
ND
ND
ND
ND
ND
ND
0.06
0.60
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.01
ND
ND
0,09
0.11
ND
0.16
041
ND
0.07 U
ND
0,21
0.06 U
0.20
ND
ND
0.05 U
ND
ND
ND
CANJ 1621 1
11/19/98
12/8798
L8LH008
ppbv
3.01
0,91
0.64
0.62
ND
ND
0.09
ND
ND
ND
0.28
ND
ND
0.17
0.09
ND
ND
1.02
0.52
ND
ND
ND
ND
ND
ND
0.06
0.73
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
144
ND
ND
0.08 U
0.15
ND
0.19
0.51
ND
0.08 U
ND
0.27
0.09
0.27
ND
ND
0.04 U
ND
ND
ND
U = Under Detection Limit
ND = Not Detected
V = Voided
2 o(11
CANJ98.99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Camden, NJ (CANJ)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-OICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 * DICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tert>BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cll-1,2-OICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1.2 -DICHLOROETHANE
1,1,1 - TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
V • DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYU KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-OIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m.p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 • TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 -DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-8UTAD1ENE
CANJ 15217 D1
12/1/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
CANJ 16227 D2
12/fffl8
12/8/98
L8LH009
ppbv
1.86
1.19
0.59
0.98
ND
NO
0.04 U
ND
ND
2.45
0.28
ND
ND
0.15
0.09
ND
ND
032
0.37
ND
ND
NO
ND
ND
ND
0.07
0.60
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
NO
1.07
ND
ND
OJ09
0.11
ND
0.17
0X6
ND
D.09 U
ND
0.22
0.09
0.22
ND
ND
ND
ND
ND
ND
CANJ 16262
12/13/99
12/31/98
L9LV016
ppbv
3.72
2.93
0.69
0.76
ND
ND
0.14
ND
ND
ND
0.32
0.66
ND
0.21
0.09
ND
ND
1.34
0.59
ND
ND
ND
ND
ND
ND
0.12
1.00
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.61
NO
ND
0.13
0.06 U
NO
0.25
0.70
ND
0,09 U
ND
0.36
0.10
0.29
ND
ND
ND
ND
ND
ND
CANJ 16276
12/26/98
1/12/99
L9AK013
ppbv
3.76
1.72
0.66
0.66
ND
ND
0.12
ND
ND
ND
0.31
ND
ND
0.09 U
0.09
, * NO *
ND
0.73
0.52
ND
ND
ND
ND
ND
ND
0.05 U
0.86
0.06 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.23
ND
ND
0.08 U
ND
ND
0.19
047
ND
0.07 U
ND
0.26
0.08
0.20
ND
ND
ND
ND
ND
ND
Us Under Detection Ulrtl
NO = Not Detected
V = Voided
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Camden, NJ (CANJ)
Yearly Report ( September 1998 - September 1999)
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHAKE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRIUE
1,1-OICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans- 12 - OICHLOROETHYLENE
1,1 • DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHUOROPRENE
cls-12-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2- DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
12-OICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans • 1,3 • DICHLOROPROPENE
1, V • TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
12-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLQROBENZENE
ETHYLBENZENE
m.p-XYLENE
BROMOFORM
STYRENE
1,122 -TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,24-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
o - DICHLOROBENZENE
124-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
CANJ 15316
1/6/99
1/21/99
L9AU009
ppbv
1.82
1.S3
0.70
0,63
ND
NO
0.09
ND
ND
ND
0.35
ND
ND
043
0.10
ND
ND
0.52
0.06
ND
ND
ND
ND
ND
ND
0.06
0.89
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.04
ND
ND
0.08 U
0.03 U
ND
0.18
0,47
ND
0.07 U
ND
0.25
0.07 U
0418
ND
ND
ND
ND
ND
ND
CANJ 16377 D1
1/30/99
2/11/99
L9BJ007
ppbv
244
O.B9
0.65
0.62
ND
ND
0.12
ND
ND
ND
043
ND
ND
020
0.08
ND
ND
fl.57
047
ND
ND
ND
ND
ND
ND
0.06
0.64
0,07 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.22
ND
ND
0.09
0.05 U
ND
0.21
0,52
ND
0.13
ND
029
0.11
028
ND
ND
ND
ND
ND
ND
CANJ15377R1
1/30/99
2/12/99
L9BL006
ppbv
2.74
0.92
0.66
0.63
ND
ND
0.11
ND
ND
ND
046
ND
ND
0.18
0.08
" ND
ND
0.59
049
ND
ND
ND
ND
ND
ND
0.06
0.69
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.21
ND
ND
0.08 U
0.04 U
ND
0.20
0.51
ND
0.10 U
ND
027
0.08
02S
ND
ND
ND
ND
ND
ND
CANJ 13379 O2
1/30/99
2/11/99
L9BJ008
ppbv
2.39
0.84
0.71
fl.«3
ND
ND
0.12
ND
ND
ND
0.63
ND
ND
025
0.08
ND
ND
O.S1
048
ND .
ND
ND
ND
ND
ND
0.07
0.66
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.17
ND
ND
0.08 U
0.05 U
ND
020
049
ND
0,12
ND
026
0.11
0.28
ND
ND
ND
ND
ND
ND
U = Under Detection Limit
NO = Not Delected
V = Voided
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Camden, NJ (CANJ)
Yearly Report (September 1998 - September 1999)
SAMPLE SITE*
SAMPIE DATE
ANALYSIS DATE
RLE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITR1LE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-OICHLOROETHYLENE
BROMOCHLOROMETHAKE
CHLOROFORM
ETHYL tert-Birm ETHER
1,2 • DICHLOROETHANE
1,1,1 . TR1CHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 -DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYtATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1.1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
NOCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
o-XYLENE
1,3.5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p • DICHLOROBENZENE
0 • DICHLOROBENZENE
1.24-TRICHLOROBENZENE
HEXACHLORO-1,J-BUTADIENE
CANJ 15379 R2
1/30/99
2/12/99
L9BL006
ppbv
2.50
0.87
0.72
0.63
ND
ND
0.09
ND
ND
ND
0.79
ND
ND
029
0.10
ND
ND
0.50
0.52
ND
ND
ND
ND
ND
ND
0.08
0.65
0.07 U
ND
ND
ND
ND
ND
ND
ND
0.04 U
ND
ND
1.22
ND
ND
0.08 U
0.03 U
NO
0.19
047
ND
0.10 U
ND
0.2S
0.09
0.22
ND
ND
ND
ND
ND
ND
CANJ 16463
2/17/99
94/99
L9CD016
ppbv
3.29
1.10
0.55
047
ND
ND
0.14
ND
ND
ND
040
ND
ND
0.32
0.08
ND
ND
171
0.59
ND
ND
ND
ND
ND
ND
0.04 U
0.74
O.OS U
ND
ND
ND
ND
ND
ND
ND
0.07
ND
ND
1.72
ND
ND
0.12
0.14
ND
0.24
0.70
ND
0.09 U
ND
0.33
0.09
0.29
ND
ND
ND
ND
ND
ND
CANJ 15463
2/23/99
3/4/99
U9CD019
ppbV
1.27
0.35
040
0.48
ND
ND
0.02 U
ND
ND
ND
070
ND
ND
0.07 U
0.06
ND
ND
0.25
0.21
ND
ND
ND
ND
ND
ND
0.04 U
0.34
0.05 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
044
ND
ND
ND
0.03 U
ND
0.06 U
0.18
ND
0.02 U
ND
0.09
ND
0.05 0
ND
ND
• ND
ND
ND
ND
CANJ 15511
3OT99
3/17/99
L9CQ009
ppbV
143
0.41
0.54
0.64
ND
ND
ND
ND
ND
0.73
0.27
ND
ND
0.08 U
0.08
ND
ND
0.83
0.34
ND
ND
ND
ND
ND
ND
0.06
043
0.07 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
048
ND
ND
0.04 U
ND
ND
0.10
0.21
ND
0.04 U
ND
0.12
0.05 U
0.09
ND
ND
ND
ND
ND
ND
U = Under Detection Limit
NO = Not Detected
V = Voided
CANJ98.99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Camden, NJ (CANJ)
Yearly Report ( September 1998 - September 1999)
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-OICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - V - DICHLOROETHYLENE
1.1-DICHLOROETHANE
METHYL tert-8UTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cIs-U-OICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1.2'DICHLOROETHANE
1*1,1 • TRICHLORQETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 . DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METH ACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans • 1.3 - DICHLOROPROPENE
1,1,2 » TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETKANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
nM)-XYLENE
BROMOFORM
STYRENE
1.1,2,2 -TETRACHLOROETHANE
o-XYLENE
1,3,5-TRIMETHYLBENZENE
1A6TR1METHYLBENZENE
m - DICHLOROBENZENE
CHLDROMETHYLBENZENE
p- DICHLOROBENZENE
o. DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLOR0.1,S-BUTADIENE
CANJ 1SS3S
3/13/99
3/24/99
L9CX007
ppbv
1.79
1.13
0.63
D.70
ND
ND
0.32
ND
ND
2.65
0.29
ND
ND
0.13
0.12
ND
ND
0.32
1.21
ND
ND
ND
ND
ND
ND
0.07
0.70
0.08 U
ND
ND
ND
ND
ND
ND
ND
0.07
ND
ND
1.28
ND
ND
0.09
ND
ND
0.24
0.66
ND
0.10
ND
0.34
0.12
0.29
ND
ND
ND
ND
ND
ND
CANJ 15624 D1
3/26/99
4/16/99
L9DP012
ppbv
1.37
043
0.50
056
ND
ND
ND
ND
ND
No
0.24
ND
ND
0.12
0.07
ND
ND
0.31
0.52
NO
ND
ND
ND
NO
ND
0.04 U
0.36
0.05 U
ND
ND
ND
NO
ND
ND
ND
MO
ND
ND
0.57
ND
ND
0.05 U
0.05 U
ND
0.11
037
ND
0.05 U
ND
0.15
0.06 U
0.14
ND
ND
ND
ND
ND
ND
CANJ 16624 R1
3/25/99
4/21/99
L9DU009
ppbv
1.46
OA7
0.65
0.64
ND
ND
ND
ND
ND
ND
0.74
ND
ND
0.33
0.09
ND
ND
0.27
0.54
ND
ND
ND
ND
ND
ND
0.05 U
0.39
0.09 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.65
ND
ND
0.06 U
0.04 U
ND
0.13
0.32
ND
0,06 U
ND
0.16
0.08
0.18
ND
ND
ND
ND
ND
ND
CANJ 16626 D2
3/28/99
4/22/99
L9DV006
ppbv
1.59
0.47
0.68
0.67
ND
ND
ND
ND
ND
ND
0.69
ND
ND
0.38
0.09
ND
ND
0.29
0.55
ND
ND
ND
ND
ND
ND
0,05 U
042
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.66
ND
ND
04)7 U
0.06 U
ND
0.13
0.31
ND
0.06 U
ND
0.16
0.06 U
0.16
ND
ND
ND
ND
ND
ND
U = Under Detection Limit
ND = Not Detected
V-Voided
6 of 11
CANJ98.99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Camden, NJ (CANJ)
Yearly Report ( September 1998 - September 1999)
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLQROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHAKE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans- 1,2 -DICHI.OROETHYLENE
1,1-DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL terfcBUTYL ETHER
1,2 - DICHLOROETHANE
1,1,1 • TRICHLOROETOANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1,3 - DICHLOROPROPENE
METHYL 1SOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTAKE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m.p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
o- DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
CANJ 15626 R2
3/26/99
4/21/99
L9DU010
ppbv
1.50
045
0.64
0.69
ND
ND
ND
ND
ND
ND
0.68
ND
ND
0.30
0.09
ND
ND
0.29
0.52
ND
ND
ND
ND
ND
ND
0.04 U
0.39
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.66
ND
ND
0.06 U
0.04 U
ND
0.13
0.31
ND
0.07 U
ND
0.16
0.07 U
0.19
ND
ND
ND
ND
ND
ND
CANJ 15686
4/18/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
CANJ 15709
4/30/99
5/26/99
L9EZ011
ppbv
1.61
0.65
0.76
0.93
ND
ND
. ND
ND
ND
ND
0.29
0.91
ND
0.09 «
0.11
ND
ND
0.64
0.66
ND
ND
ND
ND
ND
ND
0.07
043
0.10
ND
ND
ND
ND
ND
ND
ND
0.09
ND
ND
0.78
NO
ND
0.06 U
ND
ND
0.15
0.34
ND
0.07 U
ND
0.19
0.08
0.17
ND
ND
ND
ND
ND
ND
CANJ 16788
6/24799
6/7/99
L9FG011
ppbv
1.81
1.62
0.64
0.86
0.02 U
ND
0.11
0.03 U
0.03 U
ND
0.39
1.15
ND
0.16
0.10
ND
ND
1.15
0.97
ND
ND
ND
ND
ND
ND
0.09
0.64
0.10
ND
ND
ND
ND
ND
ND
ND
0.11
ND
ND
1.36
ND
ND
0.20
0.08 U
ND
0.21
0.61
ND
0.09 U
ND
0.28
0.10
0.27
ND
ND
0.07 U
ND
ND
ND
U = Under Detection Limit
NO = Not Detected
V« Voided
7 of 11
CANJ98.99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Camden, NJ (CANJ)
Yearly Report (September 1998 • September 1999)
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRIUE
1,1-DICHLOROETHENE
METHYLEKE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans -1,2 - DICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL twfrBUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cIs-V-OICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL Urt-CUTYL ETHER
1,2- DICHLOROETHANE
1,1*1 • TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 • DICHLOROPROPANE
ETHYL ACRYLATE
BRQMODWHiOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL tSOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1.1,2 • TRJCHLOROETHANE
TOLUENE
OIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
o - DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
CANJ 15902
6/6/99
6/24/99
L9FW009
ppbv
1.12
1.08
0.61
037
ND
ND
0.04 U
04)5
ND
ND
0.28
ND
ND
0.11
0.10
ND
ND
1.18
1.06
ND
ND
ND
ND
ND
ND
0.07
0.47
0.05 U
0.02 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.77
ND
ND
0.12
0.03 U
ND
0.14
0.38
ND
04)6 U
ND
0.18
0.07 U
0.16
ND
ND
0.08
ND
0.01 U
ND
CANJ 15995
6/17/99
7/14/99
L9GN009
ppbV
0.97
0.85
0.80
1.00
0.02 U
NO
0.04 U
0.04
ND
ND
0.38
0.94
ND
0.10
0.12
ND
ND
0X2
1.55
ND
ND
NO
0.01 U
ND
ND
0.08
0.33
0.10
ND
ND
ND
ND
ND
ND
ND
NO
ND
NO
0.64
ND
ND
0.07 0
0.07 U
ND
0.11
0.24
ND
0.07 tl
ND
0.13
0.07 U
0.17
ND
ND
0.02 U
ND
ND
ND
CANJ 16000
7/5/99
7/20799
L9GT011
ppbv
1.03
2.04
0.74
1.01
0.01 U
ND
0.05
0.03 U
ND
OXT
0.35
ND
ND
0.10
0.11
ND
ND
0.84
1.26
ND
ND
ND
ND
ND
ND
0.07
042
0.09 U
ND
ND
ND
ND
0.06
ND
ND
0.18
ND
ND
1.33
ND
ND
0.11
0.03 U
ND
0.17
37.00
ND
0.10 U
ND
0.19
0.07 U
0.17
ND
ND
0.09
ND
ND
ND
CANJ 16036
7/11/99
7/28/99
L9CI009
ppbv
0.63
fl.41
0.66
0.71
ND
ND
0.02 U
ND
ND
ND
0.32
OJO
ND
0.09 U
0.12
ND
ND
0,34
0.52
ND
ND
ND
ND
ND
ND
0.06
0.29
0.10
ND
ND
ND
ND
0.07
ND
ND
ND
ND
ND
OM
ND
ND
0.06 U
0.08 U
ND
0.09 U
0.19
ND
0.0$ U
ND
0.11
0.05 U
«,10
ND
ND
0.03 U
ND
ND
ND
U = Under Detection Limit
ND » Not Detected
V = Voided
6 of 11
CANJ98.99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Camden, NJ (CANJ)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITES
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
ACETYLENE
PRQPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans • 1,2 - WCHLOROETHYLENE
1,1 • DICHLOROETHANE
METHYL tert-BUTYC ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-OICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYLteifcBUTYi ETHER
1,2 - DICHLOROETHANE
1,1.1 • TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1.2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL 1SOBUTYL KETONE
trans - 1,3 • DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-OIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLDROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1.1,2,2 • TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0- DICHLOROBENZENE
1.2.4.TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
CANJ 16187
7/23/99
8/10/99
L9HJ015
ppbv
1.28
1.31
0.77
1.Z1
ND
ND
0.04 U
0/M
0.11
ND
046
ND
ND
0.20
0.14
ND
ND
1.33
1.87
ND
ND
ND
ND
ND
ND
0.08
0.66
0.11
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.17
ND
ND
0.19
0.06 U
ND
0.19
0.41
ND
0.07 U
ND
0.20
0.07 U
0,17
ND
ND
0.03 U
ND
ND
ND
CANJ 16241
8/4/99
8/11/99
L9HJ017
ppbv
1.16
0.70
0.82
1.14
ND
ND
0.04 U
ND
ND
ND
0.3S
ND
ND
0.16
0.11
ND
ND
0.80
0.64
ND
ND
ND
ND
ND
ND
0.07
0.39
0,11
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.71
ND
ND
0.07 W
0.05 U
ND
0.13
0.33
ND
0.05 U
ND
0.16
0.06 U
0.1S
ND
ND
0.06 U
ND
ND
ND
CANJ 16363
8/16/9$
9/2/99
L9IB007
ppbv
1.19
0.72
0.68
0.98
ND
ND
ND
0.05
ND
ND
0.39
ND
ND
0.13
0.10
ND
ND
1.62
1.05
ND
ND
ND
ND
ND
ND
0.07
0.57
0.10
ND
ND
ND
ND
0.02 U
ND
ND
ND
ND
ND
1.66
ND
ND
0.11
0.08 U
ND
0.26
0,54
ND
0.19
ND
0.29
0.09
0.22
ND
ND
0.03 U
ND
ND
ND
CANJ 16601
8/28/99
9/16799
L9tN016
ppbv
1.53
6.23
0.80
1.01
ND
ND
0.06
0.1S
ND
ND
0.36
1.03
ND
0.14
0.10
ND
ND
1.65
0.77
ND
ND
ND
ND
ND
ND
0.08
0.69
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.15
ND
ND
0.15
0.07 U
ND
0.18
0.49
ND
0.11
ND
0.25
0.09
0.23
ND
ND
0.08
ND
ND
ND
U » Under Detection Limit
ND= Not Detected
V = Voided
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Camden, NJ (CANJ)
Yearly Report (September 1998 - September 1999)
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
RUE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETOHITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DtCHLOROETHYLEKE
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cl«-1,2-DICHLOROETHYLENE
BROMOCHLOROM ETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 - DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
teit-AMYL METHYL ETHER
V * DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 -DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 • DICHLOROPROPENE
1,1,2 <• TRICHLOROETHANE
TOLUENE
DIBROMOCHbORQMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
U^TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYL8ENZENE
p - DICHLOROBENZENE
0 -DICHLOROBENZENE
1 ,24-TRICHLOROBENZENE
HEXACMLORO-1.3-BUTAOIENE
CANJ 16713
9/9/99
9/22/99
L9IV012
ppbv
1.58
0.8S
0.69
1.15
ND
ND
0.08
NO
ND
ND
0.33
1,14
ND
0.19
0.12
NO
ND
1.13
0.59
ND
ND
ND
ND
ND
ND
0.08
0.51
8.11
ND
ND
ND
NO
ND
ND
ND
NO
ND
ND
1.08
ND
ND
0.1T
0.05 U
ND
0.17
0.48
ND
0.09 U
ND
0.24
0.12
047
ND
ND
0.07 U
ND
ND
NO
CANJ 16790 O1
9/16/99
10/12/99
L9JK019
ppbv
0.75
1.28
0.81
1.02
ND
ND
0.11
ND
ND
ND
0.37
0.62
ND
0.29
0.11
ND
ND
140
0.54
ND
ND
ND
ND
ND
ND
0.07
0.56
0.09 U
ND
ND
ND
ND
0.08
ND
ND
ND
ND
ND
2.01
ND
ND
0.15
0.20
ND
0.25
0.68
ND
0.07 U
ND
0.33
0.11
0.30
ND
ND
0.05 U
ND
ND
ND
CANJ 16790 R1
9/15/99
10/18/99
L9JL014
ppbV
0.71
1.07
0.66
0.85
ND
ND
0.08
ND
ND
ND
0.32
047
ND
0.25
0.08
ND
ND
1.17
048
ND
ND
ND
ND
ND
ND
0.06
048
0.07 U
ND
ND
ND
ND
0.06 U
ND
ND
ND
ND
ND
1.61
ND
ND
0.13
0.17
NO
0.19
0.57
ND
0.07 U
ND
0.26
0.08
0.24
ND
ND
0.04 U
ND
ND
ND
CANJ 16791 D2
9/16/99
10/12/99
L9JK020
ppbv
0.72
1.22
0.75
0.67
ND
ND
ND
ND
ND
2.83
0.33
D.62
ND
0.30
0.09
ND
ND
1.34
0.60
ND
ND
ND
0.03 U
ND
ND
0.08
0.57
0.10
ND
ND
ND
ND
0.06
ND
ND
ND
ND
ND
1.99
ND
ND
0.14
0.19
ND
0.24
0.69
ND
0.04 U
ND
042
0.11
0.28
ND
ND
0.04 U
ND
ND
ND
U = Under Detection limit
NO = Not Detected
V = Voided
CANJ98.99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Camden, NJ (CANJ)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLOROOIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METH YLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans- 1,2 *OICHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2-DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 • DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans -1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
D1BROMOCHLOROMETHANE
1,2-OIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
mf - XYLENE
BROMOFORM
STYRENE
1,1,2.2 - TETRACHLOROETHANE
o- XYLENE
1,3,5-TRIMETHYLBENZENE
1.2ATRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0- DICHLOROBENZENE
1.2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTAOIENE
CANJ 1679f R2
9/16/99
10/13/99
L9JL015
ppbv
0.83
1.27
0.80
0.73
ND
ND
ND
ND
ND
3.33
0.36
O.S2
ND
0.28
0.10
ND
ND
1X3
0.74
ND
ND
ND
0.03 U
ND
ND
0.07
0.60
0.10
ND
ND
ND
ND
0.07
ND
ND
ND
ND
ND
2.07
ND
ND
0.16
0.21
ND
0.25
0.71
ND
0.05 U
ND
043
0.10
0.28
ND
ND
0.05 U
ND
ND
ND
U = Under Detection Umll
ND - Not Delected
V = Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - El Paso, TX (EPTX)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITE*
SAMPLE DATE
ANALYSIS PATE
FILE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETOKITRJUE
TRICHLOROFLUOROMETHANE
ACRYLOKITR1LE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans • 1,2 - DICHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-OICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 - DICHLOROETHANE
1,1,1 • TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 .TRICHLOROETHANE
TOLUENE
OIBROMOCHLOROM ETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLORQBENZENE
ETHYLBENZENE
m.p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,24-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROM ETHYLBENZENE
p- DICHLOROBENZENE
0. DICHLOROBENZENE
1,24-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
EPTX 14893
6/14/98
10/14/98
L8JM012
ppbv
3.02
1.16
0.78
1.10
ND
ND
0.12
ND
ND
ND
1.20
0.91
ND
345
0.10
ND
ND
ND
1.32
ND
ND
ND
ND
ND
ND
0.09
1.13
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.25
ND
ND
0.11
ND
ND
040
143
ND
0.09 U
ND
048
0.15
043
ND
ND
0.08
ND
ND
ND
fPTX 15000 i
9/20/98
10/15/98
L8J0007
ppbv
2.71
1.00
0.63
0.84
ND
ND
0.13
ND
ND
ND
0.53
0.67
ND
142
0.08
ND
ND
0.12
1.54
ND
ND
ND
ND
ND
ND
0.09
0.97
0.11
ND
ND
ND
ND
ND
ND
ND
0.12
ND
ND
3.22
ND
ND
0.12
0.14
ND
0.39
0.89
ND
0.26
ND
042
0.11
0.3S
ND
ND
ND
ND
ND
ND
iPTX1SQ$6
10/2/98
10/22/98
L8JV012
ppbv
3.63
1.55
0.58
0.67
ND
ND
0.17
ND
ND
ND
0.26
ND
ND
0.69
0.09
ND
ND
0.76
0.51
ND
ND
ND
ND
ND
ND
0.05 U
1.54
0.07 U
0.59
ND
ND
ND
ND
ND
ND
ND
ND
ND
241
ND
ND
0.10
ND
ND
042
1.25
ND
0.11 0
ND
0.61
0.15
0.59
ND
ND
ND
ND
ND
ND
EPTX 15128
10/14/98
11/3/98
L8KC008
ppbv
4.06
1.76
0.71
0.90
ND
ND
0.28
ND
ND
ND
0.30
1.15
ND
0.60
0.09
^ NO
ND
0.66
1.39
ND
ND
ND
ND
ND
ND
0.05 U
1.21
0.07 U
0.52
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.58
ND
ND
0.10
ND
ND
041
1.15
ND
0.12
ND
0.56
0.17
0.51
ND
ND
0.07 U
ND
ND
ND
U = Under Detection Limit
ND = Not Detected
V = Voided
lot 11
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - El Paso, TX (EPTX)
Yearly Report (September 1998 - September 1999)
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETON1TR1LE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-OICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans • 1,2 - DICHLOROETHYLENE
1,1 • DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 - DICHLOROETHANE
1,1.1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2-DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 -TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0- DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
EPTX1S149
10/26/98
11/3/98
L8KC014
ppbv
6.52
2.43
0.76
1.14
ND
ND
0.41
ND
ND
ND
0.36
1.64
ND
1.12
0.10
ND •
ND
0.78
0.74
ND
ND
ND
ND
ND
ND
0.05 U
1.40
0.10
0.54
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.62
ND
ND
0.11
ND
ND
0.47
1.32
ND
0.14
ND
0.67
0.19
0.59
ND
ND
0.06 U
ND
ND
ND
EPTX 1$183
11tf/98
11/18/98
L8HR013
ppbv
6.13
1.71
0.59
0.87
ND
ND
0.29
ND
ND
ND
0.29
ND
ND
1.40
0.10
ND
ND
0.59
0.65
ND
ND
ND
ND
ND
ND
0.06
1.41
0.07 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.24
ND
ND
0.11
ND
ND
DM
1.15
ND
0.11
ND
0.58
0.16
0.49
ND
ND
ND
ND
ND
ND
EPTX 16207
11/19/98
11/30/98
L8K$017
PPbv
7.64
2.26
0.66
0.80
ND
ND
0.38
ND
ND
ND
0.29
ND
ND
0.81
0.12
ND
ND
0.92
0.80
ND
ND
ND
ND
ND
ND
0.06
1.82
0.07 U
0.77
ND
ND
ND
ND
ND
ND
ND
ND
ND
3.13
ND
ND
0.19
ND
ND
0.55
1.52
ND
0.19
ND
0.76
0.43
1.27
ND
ND
ND
ND
ND
ND
EPTX1B233
12/1/98
12/8/98
L8LH015
ppbv
8.11
2.70
0.71
0.77
ND
ND
045
ND
ND
8.05
0.30
ND
ND
0.97
0.09
ND
ND
1.06
1.13
ND .
ND
ND
ND
ND
ND
0.06
2.25
0.09
0.80
ND
ND
ND
ND
ND
ND
0.08
ND
ND
4.86
ND
ND
0.28
0.04 U
ND
0.77
2.00
ND
0.19
ND
0.95
0.27
0.85
ND
ND
0.10
ND
ND
ND
U = Under Detection Ijmll
ND = Not Detected
V = Voided
TX98.99
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - El Paso, TX (EPTX)
Yearly Report (September 1998 - September 1999)
SAMPUSTTE*
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITR1LE
TRICHLOROFLUOROMETHANE
ACRYLONITR1LE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans * 1,2 - DICHLOROETHYLENE
1.1 - DICHLOROETHANE
METHYt ttrt-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPREHE
CIS-1.2-OICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 - DICHLOROETHANE
1,1,1 -TRICHLOROETHAHE
BENZENE
CARBON TETRACHLORIDE
teit-AMYL METHYL ETHER
1,2 . OICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYiATE
els -1.3 . DICHLOROPROPENE
METHYL ISOBUTYt KETONE
trans - 1,3 - DICHLOROPROPENE
1.1.2 -TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-OIBROMOETHANE
NOCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1.1,2,2 -TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,24-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLflENZENE
p - DICHLOROBENZENE
0- DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
EPTX 1526$
12/13/98
12/31(98
U8LV016
ppbv
18.89
4.72
0.85
0.85
ND
ND
0.79
ND
ND
ND
0.33
ND
ND
1.03
0.11
ND
ND
1.69
0.82
ND
ND
ND
ND
ND
ND
0.07
3.36
0.11
0.94
ND
ND
ND
ND
ND
ND
ND
ND
ND
6.19
ND
ND
041
0.05 U
ND
1.04
2.79
ND
0.19
ND
1.27
0.34
1.08
ND
ND
0.12
ND
ND
ND
EPTX 15290 *
12/25/98
12/25/99
L9AK016
ppbv
10.50
140
0.70
1.0S
ND
ND
0.52
ND
ND
ND
0.31
1.16
ND
1.66
0.11
ND
ND
1.22
1.19
ND
ND
ND
ND
ND
ND
0.05 U
2.08
0.05 U
1.05
ND
ND
ND
ND
ND
ND
ND
ND
ND
3.88
ND
ND
0.29
0.07 U
ND
0.61
1.81
ND
0.15
ND
0.87
0.25
0.72
ND
ND
0.03 U
ND
ND
ND
EPTX 15343
1/6/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
EPTX 15389
1/30/99
2/12/99
L9BL010
ppbv
6.03
1.89
0.67
0.78
ND
ND
0.35
ND
ND
11.63
0.31
ND
ND
0.90
0.09
ND
ND
0.73
0.82
ND
ND
ND
ND
ND
ND
0.05 U
143
0.08 . U
0.65
ND
ND
ND
ND
ND .
ND
0.05
ND
ND
246
ND
ND
0.18
0.02 U
ND
042
1.1S
ND
0.12
ND
0.54
0.18
0.50
ND
ND
0.02 U
ND
ND
NO
U = Under Detection Limit
ND = Not Detected
V = Voided
Tx9B_99
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - El Paso, TX (EPTX)
Yearly Report (September 1998 - September 1999)
SAMPLE SfTE#
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tett-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 -DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2-DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 • DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - OICHLOROPROPENE
1,1,2 • TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
K-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,24-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p • DICHLOROBENZENE
0- DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
EPTX 16401 01
2/11/99
2/17/99
L9BQ012
ppbv
2.48
0.99
0.61
0.58
ND
NO
0.18
ND
ND
ND
0.27
ND
ND
0.58
0.09
«- ND
ND
0.25
0.31
ND
ND
ND
ND
ND
ND
0.05 U
0.73
0.07 U
0.23
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.06
ND
ND
0.09
ND
ND
0.18
0.45
ND
0.06 U
ND
0.23
0.07 U
0.20
ND
ND
ND
ND
ND
ND
EPTX 15«1 R1
2711/99
2/23/99
L9BW010
ppbv
2.41
0.98
0.60
0.61
ND
ND
0.15
ND
ND
ND
0.28
ND
ND
0.59
0.09
ND
ND
0.29
0X1
ND
ND
ND
ND
ND
ND
0.06
0.76
0.06 U
0.24
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.07
ND
ND
0.07 U
ND
ND
0.18
0.45
ND
0.06 U
ND
0.24
0.07 U
0.20
ND
ND
ND
ND
ND
ND
EPTX 15403 D2
2/11/99
2/17/99
L9BQ013
ppbv
243
1.09
0.62
0.73
ND
ND
0.09
ND
ND
ND
0.28
ND
ND
0.54
0.07
ND
ND
0.19
0.52
ND
ND
ND
ND
ND
ND
0.06
0.78
0.10
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.93
ND
ND
0.07 U
ND
ND
0.18
0.45
ND
0.02 U
ND
0.22
0.07 U
0.18
ND
ND
ND
ND
ND
ND
EPTX 15403 R2
2/11/99
2/23/99
L9BW011
ppbv
2.69
1.17
0.66
0.77
ND
ND
0.11
ND
ND
ND
0.29
ND
ND
0.57
0.08
NP>.,
ND
0.20
0.71
ND
ND
ND
ND
NO
ND
0.04 U
0.75
0.09
0.08
ND
ND
NO
ND
ND
ND
ND
ND
ND
0.90
ND
ND
0.07 U
ND
ND
0.17
0.44
ND
0.02 U
ND
021
0.07 U
0.15
ND
ND
ND
ND
ND
ND
U = Under Detection Until
ND = Not Detected
V = Voided
TX98J9
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - El Paso, TX (EPTX)
Yearly Report ( September 1998 - September 1999)
SAMPLE SITE*
SAMPLE DATE
ANALYSIS PATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHAKE
CHLOROETHANE
ACETONITR1LE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE .
1,1-DICHUOROETHENE
METHYLEHE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1.2 - DICHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL tert'BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2-DICHLOROETHANE
1,1,1 'TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 -OICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1.3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans • 1,3 - DICHLOROPROPENE
1,1.2 'TRICHLOROETHANE
TOLUENE
DIBROWOCHLOROMETHANE
1.2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,24-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 .DICHLOROBENZENE
1,24-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
EPTX 15433
2/17/99
3/4/99
L9CD010
ppbv
7.29
2.69
0.64
0.72
ND
ND
0.47
ND
ND
ND
0.28
0.83
ND
0.81
0.09
ND
ND
1.09
2.00
ND
ND
ND
ND
ND
ND
04)5 U
1.79
0.04 U
ND
ND
0.06
ND
0.03 U
ND
ND
0.31
ND
ND
2.98
ND
ND
0.12
0.05 U
ND
048
1.39
ND
0.09 U
ND
045
0.19
0.58
ND
ND
0.09
ND
0.18
0.19
£PTX 15465
2/23/99
3/5/99
L9CD017
ppbv
5.57
2.06
044
0.60
ND
ND
0.32
ND
ND
ND
0.21
ND
ND
0.68
0.07
ND
ND
0,77
0.54
ND
ND
ND
ND
ND
ND
0.03 U
1.48
0.05 U
0.59
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.29
ND
ND
0.09
0.03 U
ND
0.36
1.09
ND
0.06 U
ND
049
0.13
0.38
ND
ND
0.04 U
ND
ND
ND
EPTX 15455
3/1/99
3/10/99
L9CJ012
ppbv
5.52
2.04
0.65
0.87
ND
ND
0.33
ND
ND
ND
0.32
0.92
ND
0.79
0.08
ND
ND
0.87
0.84
ND
ND
ND
ND
ND
ND
0.05 U
1.34
0.07 U
0.64 U
ND
ND
ND
ND
ND
ND
ND
ND
ND.
2.72
ND
ND
0.17
ND
ND
045
1.39
ND
0.07 U
ND
0.67
0.33
0.99
ND
ND
ND
ND
ND
ND
EPTX 15495
3/7/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
.-V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
U = Under Detection Limit
NO = Not Detected
V = Voided
5 of 11
1x98.99
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - El Paso, TX (EPTX)
Yearly Report (September 1998 - September 1999 )
SAMPLE SITES
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITfULE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
CIS-1.2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL Urt-BUTYL ETHER
1,2 - DICHLOROETHANE
1,1,1 *TRK5HLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 * DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1.3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 -TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBEHZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1.2,2 -TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,24-TRIMETHYLBENZENE
m-DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1,24-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
EPTX 15527
3/13/99
3/24/99
L9CX009
PPbv
4.09
148
0.64
0.73
ND
ND
0.20
ND
ND
ND
0.29
0.66
ND
0*6
0.08
ND
ND
042
0.98
ND
ND
ND
ND
ND
ND
0.05 . U
1.16
0.07 U
0.37
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.83
ND
ND
0.10
ND
ND
0.31
0.90
ND
0.07 U
ND
044
0.12
0.36
ND
ND
0.02 U
ND
ND
ND
EPTX 15525
3/19/99
3/24/99
L9CX010
ppbv
3.38
1.24
0.63
0.66
ND
ND
0.14
ND
ND
ND
0.28
O.S8
ND
0.68
0.09
, . - ND
ND
0.52
0.63
ND
ND
ND
ND
ND
ND
0.05 U
1.03
0.07 U
042
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.22
ND
ND
0.12
ND
ND
0.31
0.87
ND
0.08 U
ND
0.41
0.11
0.34
ND
ND
0.03 U
ND
ND
ND
EPTX 1561$
3/31/99
4/16/99
L9DP015
PPbv
145
0.35
0.59
0.64
ND
ND
ND
ND
ND
8.13
0.29
ND
ND
0.38
0.09
ND
ND
ND
3.39
ND
ND
ND
ND
ND
ND
0.07
047
0.08 U
ND
ND
ND
ND
0.10
ND
ND
ND
ND
ND
046
ND
ND
0.11
ND
ND
047
0.60
ND
1.81
ND
0.32
0.08 U
0.08 U
ND
ND
ND
ND
ND
ND
EPTX 15534
4/6/99
4/22/99
L9DV008
ppbv
11.29
3.77
0.74
0.81
ND
ND
0.65
ND
ND
ND
0.30
ND
ND
0.8S
0.10
ND . ,
ND
0.71
2.02
ND
ND
ND
ND
ND
ND
0.06 U
3.09
0.07 U
0.58
ND
ND
ND
0.11
ND
ND
ND
ND
ND
7.33
NO
ND
0.31
0.05 U
ND
1.03
3.19
ND
0.19
ND
1.49
0.36
1.11
ND
ND
0.15
ND
ND
ND
U = Under Detection Unnil
ND = Not Detected
V n Voided
Tx98 99
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - El Paso, TX (EPTX)
Yearly Report ( September 1998 - September 1999)
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILE MAMIE
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-OICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans • 1.2 - DICHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL tert-BOTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BOTYL ETHER
1,2-DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2-DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1.2 • TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1.2-OIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
tn,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
O.XYLENE
1,3,5-TRIMETHYLBENZENE
1,24-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZEHE
p - DICHLOROBENZENE
o- DICHLOROBENZENE
1,24-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
EPTX 1556? Of
4/12/99
5/10/99
L3EJ010
ppbv
747
2.70
0.77
0.80
ND
ND
042
0.10
ND
ND
0.37
ND
ND
043
0.10
ND
ND
0.36
1.76
ND
ND
ND
ND
ND
ND
0.07
2.21
0.09 U
0.28
ND
ND
ND
ND
ND
ND
0.12
ND
ND
4.88
ND
ND
0.21
0.06 U
ND
0.80
2.24
ND
0.16
ND
1.09
0.27
0.79
ND
ND
0.06 U
ND
ND
NO
EPTX 15668 R1
4/12/99
5/12/99
L9EL009
ppbv
8.87
2.94
0.83
0.89
ND
ND
041
0.11
ND
ND
041
ND
ND
0.67
0.11
ND
ND
0.36
1.75
ND
ND
ND
ND
ND
ND
0.07
2.34
0.10
0.31
ND
ND
ND
ND
ND
ND
0.13
ND
ND
S.12
ND
ND
0.24
0.04 U
ND
0.84
2.35
ND
fl.15
ND
1.11
0.28
0.84
ND
ND
0.06 U
ND
ND
ND
gPTX 15670 D2
4/12/99
5/10/99
L9EJ011
ppbv
7.55
2.69
0.73
0.76
ND
ND
040
0.11
ND
ND
0.38
ND
ND
0.78
0.10
ND
ND
0.35
1.75
ND
ND
ND
ND
ND
ND
0.07
2.18
0.09 U
0.28
ND
ND
ND
ND
ND
ND
0.12
ND
ND
4.7$
ND
ND
033
0.04 U
ND
0.80
221
ND
0.1S
ND
1.06
0.27
0.80
ND
ND
0.07 U
ND
ND
ND
EPTX 1567Q R2
4/12/99
5/12/99
L9EL010
PPbv
8.57
2.80
0.75
0.80
ND
ND
040
0.10
ND
ND
0.39
ND
ND
0.38
0.11
NO
ND
0.34
133
ND
ND
ND
ND
ND
ND
0.07
2.36
0.09 U
0.30
m
ND
ND
ND
ND
ND
0.13
ND
ND
4.82
ND
ND
0.23
0.04 U
ND
0.81
2.30
ND
0.15
ND
1.09
0.27
0.80
ND
ND
0.06 U
ND
ND
ND
U = Under Detection Limit
ND = Not Detected
V = Voided
Tx9a_99
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - El Paso, TX (EPTX)
Yearly Report ( September 1998 - September 1999)
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITR1LE
TRICHLOROFLUOROMETHANE
ACRYLONITR1LE
1,1-OICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans • V • DICHLOROETHYLENE
1.1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,2-OICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 - DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TR1CHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m.p-XYCENE
BROMOFORM
STYRENE
1.1,2,2 - TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRlMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0- DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
EPTX 15688
4/16/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
EPTX 15702
4/24)99
5/18/99
L9ER008
PPbV
2.96
1.04
0.76
0.88
ND
NO
0.11
ND
ND
ND
0.36
ND
ND
8,70
0.10
ND
ND
ND
1.13
ND
ND
ND
ND
ND
ND
0.08
0.98
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.83
ND
ND
0.12
ND
ND
0.31
0.83
ND
0.08 U
ND
0.42
0.12
0.31
ND
ND
ND
ND
ND
ND
EPTX 16723 01
5/6/99
5/19/99
L9ER014
ppbv
6.22
2.13
0.75
0.76
ND
ND
0.27
ND
ND
38.S3
0.34
ND
ND
OM
0.10
NO r
ND
ND
0.77
ND
ND
ND
ND
ND
ND
0.08
1.86
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
4.21
ND
ND
020
0.04 U
ND
0.60
1.75
ND
0.33
ND
0.84
0.20
0.68
ND
ND
0.04 U
ND
ND
ND
EPTX 16723 R1
5/6/99
6/19/99
L9ES008
ppbv
6.33
2.14
0.75
0.77
ND
ND
0.29
ND
ND
43.09
0.35
ND
ND
0.44
0.10
ND
ND
ND
0.78
ND
ND
ND
ND
ND
ND
0.08
1.82
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
4.29
ND
ND
0.17
0.04 U
ND
0.62
1.78
ND
0.33
ND
0.85
0.20
0.67
ND
ND
0.05 U
ND
ND
ND
U = Under Detection Limit
ND = Not Detected
V = Voided
7x98.99
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - El Paso, TX (EPTX)
Yearly Report ( September 1998 - September 1999)
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYUENE
DICHLORODIFLUOROMETHANE
CHLOROMETHAKE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOM ETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITR1LE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,2-OICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1.2- DICHLOROETHANE
1.1.1 -TRtCHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 • DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1.2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m.p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 -TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,24-TRIMETHYLBENZENE
m . DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
o - DICHLOROBENZENE
1£4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
EPTX 16725 02
6/6/99
6/19/99
L9ER016
ppbv
6.21
2X19
0.73
0.72
NO
ND
0.27
ND
ND
44.19
042
ND
ND
0.18
0.09
ND
ND
ND
0.78
ND
ND
ND
ND
ND
ND
0.07
131
0.07 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
4.32
ND
ND
0.20
0.05 U
ND
0.64
1.82
ND
0.75
ND
0.87
0.22
0.64
ND
ND
0.05 U
ND
ND
ND
EPTX 15725 R2
5/6/99
6/19/99
L9ES009
ppbv
6.20
2.08
0.73
0.73
ND
ND
0.28
ND
ND
48.10
043
ND
ND
0.18
0.08
ND
ND
ND
0.78
ND
ND
ND
ND
ND
ND
0.08
1.80
0.07 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
446
ND
ND
0.18
0.05 U
ND
0.62
1.83
ND
0.74
ND
0.88
0.23
0.62
ND
ND
ND
ND
ND
ND
EPTX 16731
S/18/99
6/27/99
L9EX014
ppbv
2.29
1.08
0.98
0.88
0.01 U
ND
0.11
ND
ND
ND
0.32
ND
ND
0.56
0.09
ND
ND
ND
1.33
ND
ND
ND
ND
ND
ND
0.06
0.98
0.10
ND
ND
ND
ND
ND
ND
ND
0.14
ND
ND
1.98
ND
ND
0.12
ND
ND
0.31
0.80
ND
0.09 U
ND
040
0.12
0.29
ND
ND
ND
ND
ND
ND
EPTX 15813
5/30/99
6/9/99
L9FI011
ppbv
248
1.07
0.98
0.96
0.02 U
ND
0.13
0.03 U
ND
ND
0.31
1.00
ND
0.78
0.11
ND
ND
ND
0.69
ND
ND
ND
ND
ND
ND
0.08
0.99
0.07 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.73
ND
ND
0.10
ND
ND
0.31
0.86
ND
0.09 U
ND
041
0.14
0.34
ND
ND
0.02 U
ND
ND
ND
U = Under Detection Limit
ND = Not Detected
V = Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - El Paso, TX (EPTX)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITE*
SAMPLE DATS
ANALYSIS DATE
FILE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1.2 - DICHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2-DICHLOROETHANE
1,1.1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
14 • DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1,} • DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2.2 - TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,24-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p- DICHLOROBENZENE
o- DICHLOROBENZENE
1,24-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
EPTX 15844
6/11/99
6/18/99
L9FQ016
ppbv
4.68
1.62
0.60
0.89
0.02 U
NO
0.23
ND
NO
ND
0.28
ND
ND
0.75
0.13
ND
ND
ND
0.62
ND
ND
ND
ND
ND
ND
0.06
1.59
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
3.22
ND
ND
0.15
0.01 U
ND
0.55
1.62
ND
0.12
ND
0.75
0.23
0.60
ND
ND
0.03 U
ND
ND
ND
EPTX 15933
6/23/99
7/2/99
L9GB010
ppbv
3.27
1.33
0.66
0.91
0.02 U
ND
0.20
ND
ND
ND
0.33
ND
ND
0.73
0.12
ND
ND
ND
0.90
ND
ND
ND
ND
ND
ND
0.07
1.38
0.07 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
6.13
ND
ND
0,13
0.02 U
ND
28.28
98.76
ND
0.13
ND
44.77
0.18
0.48
ND
ND
0.04 U
ND
ND
ND
EPTX 15978
7/5/99
7/20/99
L9GT010
ppbv
1.64
0.91
0.69
0.96
0.01 U
ND
0.10
ND
ND
0.52
0.31
0.87
ND
0.88
0.10
ND
ND
ND
0.58
ND
ND
ND
ND
ND
ND
0.06 U
0.66
0.08 U
ND
ND
ND
ND
ND
ND
ND
NO
ND
ND
1.31
ND
ND
0.08 U
ND
ND
0.24
0.68
ND
0.08 U
ND
0.33
0.09
0.22
ND
ND
0.05 U
ND
0.03 U
ND
EPTX 16128
7/17/99
7/28/99
L9G1013
ppbv
2.63
1.20
1.08
1.0$
0.01 U
ND
0.13
ND
ND
1.J3
043
ND
ND
0.97
0.11
NO • '•••
ND
0.09
1.92
ND
ND
ND
ND
ND
ND
0.16
142
0.10
0.07
ND
0.19
ND
0.11
ND
ND
0.27
ND
ND
546
ND
ND
0.24
0.07 U
ND
0.77
1.42
ND
045
ND
0.64
0.19
0.67
ND
ND
0.07 U
ND
0.03 U
0.02 U
U = Under Detection Limit
ND = Not Delected
V = Voided
10 of 11
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - E| Paso, TX (EPTX)
Yearly Report (September 1998 - September 1999)
SAMPLE STTE*
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNtTS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETON1TRJLE
TRICHLOROFLUOROMETHANE
ACRYLONITR1LE
1,1-OICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans . 1,2 - DICHLOROETHYLENE
1.1 - DICHLOROETHANE
METHYL teftetlTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-V-OICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-eUTYL ETHER
14 - DICHLOROETHANE
1.1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 • DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROM ETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 • DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1.2-DIBROMOETHANE
N-OCTAME
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1.2,2 - TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m-DICHLOROBENZENE
CHLOROMETHYLBENZENE
p-DICHLOROBENZENE
0-DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHtORCM,3-BUTADlENB
EPTX161$6
7/29/99
8/16/99
L9HPOOT
ppbv
3.72
6.41
0.74
1.07
ND
ND
0.19
ND
ND
ND
0.35
0.86
ND
0.68
0.11
ND
ND
04)8
0.59
ND
ND
ND
ND
ND
ND
0.06
1.20
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.65
ND
ND
0.12
ND
ND
0.45
1.21
ND
0.11
ND
0.56
0.17
046
ND
ND
0.03 U
ND
ND
ND
EPTX 1632$
a/10/99
8/16/99
L9HP012
ppbv
2.69
1.48
0.77
1.04
ND
ND
0.15
ND
ND
ND
0.34
ND
ND
0.61
0.11
ND
ND
0.08
0.61
ND
ND
ND
ND
ND
ND
0,07
1.11
0.11
0.07
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.21
ND
ND
0.12
ND
ND
0.37
1.17
ND
0.09 U
ND
0.52
0.18
0.47
ND
ND
0.01 U
ND
ND
ND
EPTX 16444
8/22/93
9/2/99
L9IB008
ppbv
2.87
1.06
1.67
0.94
ND
0.09
0.16
ND
ND
ND
0.56
ND
ND
0.67
0.10
ND
ND
0.14
1.24
ND
ND
ND
ND
ND
ND
0.10
1.29
0.09
0.13
ND
ND
ND
0.02 U
ND
ND
ND
ND
ND
4.65
ND
ND
0.13
0.03 U
ND
0.52
1.31
ND
0.27
ND
0.61
0.17
0.61
0.13
ND
0.13
ND
ND
ND
EPTX 16606
9/3/99
9/14/99
L9IN016
ppbv
2.70
1.05
0.72
1.00
ND
ND
0.15
0X15
ND
ND
0.33
0.78
ND
0.58
0.10
ND
ND
0.09
OAO
ND
ND
ND
ND
ND
ND
0.07
1.05
0.11
0.08
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.48
ND
ND
0.11
0.02 U
ND
0.33
0.86
ND
0.08 U
ND
0.42
0.11
0.30
ND
ND
0.04 U
ND
ND
NO
U = Under Detection Limit
ND » Not Delected
V = Voided
1x98.99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Garyville, LA (GALA)
Yearly Report (September 1998 - September 1999)
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1.3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1 ,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - OICHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-OICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2-DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
teit-AMYL METHYL ETHER
1.2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 -TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
12-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
o-XYLENE
1,3.5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m-DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
o-OlCHLOROBENZENE
1 2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTA01ENE
GALA 14800
9/2/98
9/25/98
L8IY018
ppbv
DM
0.56
0.71
0.71
ND
ND
ND
ND
ND
ND
1.05
ND
ND
2.31
0.08
ND
ND
ND
0.82
ND
ND
ND
ND
ND
ND
0.16
0.18
0.11
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.70
ND
ND
ND
ND
ND
0.15
0.39
ND
ND
ND
0.21
ND
0.09
ND
ND
ND
ND
ND
ND
GALA 14804
9/14/98
9/25/98
L8IY022/K8IY022
ppbv
0.53
0.54
0.73
0.76
ND
ND
ND
ND
ND
ND
0.31
ND
ND
ND
0.07
ND "
ND
ND
0.44
ND
ND
ND
ND
ND
ND
0.08
0.36
0.11
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.41
ND
ND
0.56
ND
ND
0.09 U
0.23
ND
ND
ND
0.10
ND
0.15
ND
ND
ND
ND
ND
ND
GALA 15098
9/26/98
10/22/98
L8JVOOS
ppbv
0.49
0.89
0.61
1.41
ND
ND
0.15
ND
ND
ND
0.31
ND
ND
ND
0.13
ND
ND
ND
0.70
0.98
ND
ND
ND
ND
ND
0.14
0.39
4.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.76
ND
ND
0.47
0.31
ND
0.11
0.26
ND
0.09 U
ND
0.16
0.05 U
0.13
ND
ND
ND
ND
ND
ND
GALA 161 16
10/8/98
10/22/98
L8JV021
ppbv
0.61
0.68
0.70
1.35
ND
ND
ND
ND
ND
6.23
0.29
ND
ND
0.66
0.21
ND *
ND
ND
127
ND
ND
ND
ND
ND
ND
0.36
0.39
0.08 U
ND
ND
ND
ND
ND
ND
ND
0.09
ND
ND
1.27
ND
ND
0.08 U
0.07 U
ND
0.22
0.48
ND
0.13
ND
0.28
0.07 U
0.26
ND
ND
ND
ND
ND
ND
U = Under Detection Limit
ND = Not Detected
V = Sample Voided
TX98.99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Garyville, LA (GALA)
Yearly Report (September 1998 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETQKITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 -OICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL teft-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,2-DICHLOROETHYLENe
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 -DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tart-AMYL METHYL ETHER
1.2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1.3 -DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,1 • OICHLOROPROPENE
1,1,2 • TRICHLOROETHANE
TOLUENE
D1BROMOCHLOROMETHANE
1,2-OIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
o-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m-DICHLOROBENZENE
CHLOROMETHYLBENZENE
p • DICHLOROBENZENE
o-DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTAOIENE
EPTX 16149
10/14/98
11/3/98
L8KC010
ppbv
2.20
2.38
0.91
1.39
ND
NO
ND
ND
ND
1.71
041
ND
ND
0.09 U
0.11
ND
ND
0.09
0.83
ND
ND
ND
ND
ND
ND
0.06
0.71
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
141
ND
ND
0.06 U
ND
ND
0.27
0.71
ND
0.08 U
ND
0.38
0.10
0.31
ND
ND
0.03 U
ND
ND
ND
GALA 16171
10/28/98
11/11/98
L8KK020
ppbv
1.61
5.17
0.65
1.25
ND
ND
0.52
ND
ND
ND
0.29
ND
ND
0.04 U
0.11
ND
ND
ND
0.59
2.59
ND
ND
ND
ND
ND
0.08
0.78
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.21
ND
ND
0.19
ND
ND
0.24
0.65
ND
0.07 U
ND
0.30
0.09
0.26
ND
ND
ND
ND
ND
ND
GALA 16181
11/7/98
11/18/98
L8KR014
ppbv
1.34
1.60
0.54
0.72
ND
ND
0.11
ND
ND
ND
0.25
ND
ND
0.34
0.07
ND
ND
ND
0.84
049
ND
ND
ND
ND
ND
0.15
0.73
DM V
ND
ND
ND
ND
0.08
ND
ND
0.06 U
ND
ND
3.52
ND
ND
0.24
0.13
ND
0.59
1.S8
ND
0.21
ND
0.79
0.23
0.65
ND
ND
ND
NO
ND
ND
GALA 16231
11/19/98
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
v - -- >
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
U = Under Detection Limit
ND = Not Detected
V = Sample Voided
2 of 11
Tx98_89
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Garyville, LA (GALA)
Yearly Report (September 1998 - September 1999)
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1.2 - DICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 -DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1,3 - DICHLOROPROPENE
METHYL JSOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1 ,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
o-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
o-OICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORQ-1,3
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Garyville, LA (GALA)
Yearly Report (September 1998 - September 1999)
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETOKITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-OICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
tlans - 1,2 - DICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tett-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-12-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
12- DICHLOROETHANE
1.1,1 • TRICHiOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
12 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL 1SOBUTYL KETONE
trans - 1.3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m.p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
o-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2>>TRtMETHYLBENZENE
m • DICHLOROBENZENE
CHLQRQMETHYLBENZENE
p - DICHLOROBENZENE
o- DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTAOIENE
GALA1S396R1
2/5/99
2/17/99
L9BQ007
ppbv
1^47
1,34
0.78
0.89
ND
ND
0.30
ND
ND
26.13
0.15
ND
ND
0.17
0.15
ND
ND
ND
0.64
0.94
ND
ND
ND
ND
ND
022
0.81
0.09
ND
ND
ND
ND
0.04 U
ND
ND
0.05 U
ND
ND
1.23
ND
ND
0.14
0.78
ND
0.21
0.52
ND
0.08 U
ND
025
0.10
0.22
ND
ND
ND
ND
ND
ND
GALA 16397 02
2/5/99
2/12/99
L9BL012
ppbv
1.48
150
0.79
0.86
ND
ND
0.30
ND
ND
23.11
0.77
ND
ND
0.39
0.13
ND
ND
ND
0.61
0.81
ND
ND
ND
ND
ND
023
0.72
0X19
ND
ND
ND
ND
ND
ND
ND
0.12
ND
ND
1.35
ND
ND
0.14
0.68
ND
021
0.50
ND
0.11
ND
0.24
0.07 U
021
ND
ND
ND
ND
0.03 U
ND
GALA 16397 R2
2/5/93
2/17/$9
L9BQQ08
ppbv
1.23
1.15
0.78
0.83
ND
HO
0.26
ND
ND
23.38
0.74
ND
ND
0.37
0.13
ND
ND
NO
0.66
0.89
ND
ND
ND
ND
ND
021
0.69
0.09
ND
ND
ND
ND
0.04 U
ND
ND
0.12
ND
ND
1.33
ND
ND
0.14
0.67
ND
0.19
0.48
ND
0.13
ND
025
0.10
022
ND
ND
ND
0.04 U
ND
ND
GALA 16411
2/17/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
v
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
U = Under Detection Urrtt
ND = Not Detected
Vn Sample Voided
4 of 11
Tx98 99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Garyville, LA (GALA)
Yearly Report (September 1998 - September 1999)
SAMPLE SITES
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETH YLENE
1,1-DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1.2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2-DICHLOROETHANE
1,1,1 .TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1.2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1.1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m.p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
o-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
o- DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
GALA 15459
2/23/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
• v
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
GAU 15504
3/7/99
3/17/99
L9CQ007
ppbv
0.88
0.50
0.55
0.83
ND
ND
0.19
ND
ND
ND
0.25
ND
ND
0.07 U
0.10
ND
ND
ND
0.74
0.24
ND
ND
ND
ND
ND
0.06
0.37
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.42
ND
ND
0.07 U
0.12
ND
0.09 U
0.18
ND
0.04 U
ND
0.11
0.05 U
0.11
ND
ND
ND
ND
ND
ND
GALA 15523
3/13/99
3/22/99
L9CV008
ppbv
1.11
0.67
1.10
1.02
ND
ND
0.03 U
ND
ND
S.75
0.38
ND
ND
021
0.18
- ND
ND
ND
1.23
ND
ND
ND
ND
ND
ND
0.34
0.50
0.04 U
ND
ND
ND
ND
0.05 U
ND
ND
0.08
ND
NO
1.56
ND
ND
0.11
1.11
ND
0.34
O.S2
ND
0.33
ND
0.24
0.06 U
0.1S
ND
ND
ND
ND
ND
ND
GALA 16560
3/19/99
4/14/99
L9DM014
ppbv
3.89
0.92
0.66
1.06
ND
ND
ND
ND
ND
ND
0.30
ND
ND
0.07 U
0.12
NDU •"
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Garyville, LA (GALA)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-OICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1 .2 - OICHLOROETH YLENE
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 -DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1.2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1,3 - DICHLOROPROPENE
METHYL tSOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
01BROMOCHLOROMETHANE
1,2-OIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
nw-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
o-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
6 -DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3.BUTAOIENE
OALA 16691 01
3/25799
4/13/99
L9DL018
ppbv
3.10
0.38
0.64
0.94
ND
ND
ND
ND
ND
ND
0.30
ND
ND
ND
0.09
ND
ND
ND
0.83
ND
ND
ND
ND
ND
ND
0.06
0.39
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
041
ND
ND
0.06 U
ND
ND
0.09 U
0.20
ND
0.03 U
ND
0.12
0.05 U
0.11
ND
ND
ND
ND
ND
ND
GALA 1 5591 Rt
3/26/99
4/13/99
L9DM012
ppbv
3.02
0.38
0.64
0.96
ND
ND
ND
ND
ND
ND
0.31
ND
ND
0.07 U
0.09
ND
ND
ND
0.83
ND
ND
ND
ND
ND
ND
0.07
0.39
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
041
ND
ND
0.06 U
ND
ND
0.09 U
0.19
ND
0.04 U
ND
0.11
0.05 U
0.11
ND
ND
ND
ND
ND
ND
GALA 15593 02
3/2509
4/13)99
L9DL019
ppbv
2.88
0.36
0.64
0.78
ND
ND
ND
ND
ND
2.19
0.30
ND
ND
ND
0.10
ND "
ND
ND
0.54
ND
ND
ND
ND
ND
ND
0.06
0.38
0.09
ND
NO
ND
ND
ND
ND
ND
ND
ND
ND
040
ND
ND
0.06 U
ND
ND
0.09 U
oil
ND
0.03 U
ND
0.10
0.06 U
0.11
ND
ND
ND
ND
ND
ND
GALA 15593 R2
3/26/99
4/13/99
L9DM013
ppbv
3.15
0.38
0.64
0.80
ND
ND
ND
ND
ND
2.25
0.31
ND
ND
O.OJ U
0.09
ND
ND
ND
0.64
ND
ND
ND
ND
ND
ND
0.06
0.38
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND '.•
ND
ND
042
ND
ND
0.03 U
ND
ND
0.09 U
021
ND
0.04 U
ND
0.11
0.05 U
D.11
ND
ND
ND
ND
ND
ND
U = Under Detection Limit
ND - Not Delected
V = Sample Voided
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Garyville, LA (GALA)
Yearly Report (September 1998 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 12 - OICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 -DICHLOROETHANE
1,1,1 - TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 . DICHUmOPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
o-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m . DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
o-OICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTAOIENE
GALA 15620
3/31/99
4/16/99
L9DP014
ppbv
0.77
1.31
0.62
0.84
ND
ND
0.19
ND
ND
ND
0.29
ND
ND
0.68
0.10
ND
ND
0X1
0.48
ND
ND
ND
ND
ND
ND
0.06
1.13
0.08 U
0.37
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.87
ND
ND
0.11
ND
ND
0.31
0.87
ND
0.07 U
ND
0.43
0.13
0.36
ND
ND
ND
ND
ND
ND
GALA 15662 01
4/12/99
6/10/99
L9EJ006
ppbv
0.78
0.52
0.61
0.89
ND
ND
ND
ND
ND
ND
0.28
ND
ND
0.05 U
0.08
ND
ND
ND
0.62
ND
ND
ND
ND
ND
ND
0.07
0.34
0.09 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
043
ND
ND
0.04 U
ND
ND
0.10 U
0.23
ND
0.04 U
ND
0.12
0.05 U
0.13
ND
ND
ND
ND
ND
ND
GALA 16662 R1
4712/99
5/12/99
L9ELOOS
ppbv
0.99
0.59
0.67
1.00
ND
ND
ND
ND
ND
0.00
0.30
ND
ND
0.06 U
0.10
ND
ND
ND
0.74
ND
ND
ND
ND
ND
ND
0.07
0.38
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.52
ND
ND
0.06 U
ND
ND
0.12
0.27
ND
0.05 U
ND
0.1E
0.07 U
0.14
ND
ND
ND
ND
ND
ND
GALA 16664 02
4/12/99
5/10/99
L9EJ007
ppbv
0.79
O.SO
0.59
0.76
ND
ND
ND
ND
ND
ND
0.29
ND
ND
0.07 U
0.08
ND
ND
ND
0.61
ND
ND
ND
ND
ND
ND
0.06
0.34
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.44
ND
ND
0.05 U
ND
ND
0.10 U
0.24
ND
0.04 U
ND
0.12
0.05 U
0.13
ND
ND
ND
ND
ND
ND
U = Under Detection Limit
NO = Not Detected
V = Sample Voided
Tx98_99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Garyville, LA (GALA)
Yearly Report ( September 1998 - September 1999)
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1.2 - DICHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL tcrt-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-OICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2-DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIOE
tert-AMYL METHYL ETHER
1,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 . TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-OIBROMOETHANE
&OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
o-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m-DICHLOROBENZENE
CHLOROMETHYLBENZENE
p • DICHLOROBENZENE
o • DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
G ALA 1 6664 R2
4712/99
6/10/99
L9EL006
ppbv
0.91
0.53
0.64
0.84
ND
ND
ND
ND
ND
ND
0.30
ND
ND
0.03 U
0.09
ND s
ND
ND
0.68
ND
ND
ND
ND
ND
ND
0.06
0.37
0.09 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.47
ND
ND
O.OS U
ND
ND
0.10 U
0.24
ND
0.03 U
ND
0.13
0.06 U
0.12
ND
ND
ND
ND
ND
ND
GALA 15690
4/18/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
GALA 16692
4/24/99
ppbv
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
NS
GALA 15740
4/30/99
6/18/99
L9ER009
ppbv
0.91
0.55
0.86
1.06
ND
ND
ND
ND
ND
ND
0.30
ND
ND
0.24
0.20
ND
ND
ND
1.01
ND
ND
ND
ND
ND
ND
0.32
0.31
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.50
ND
ND
0.06
0.50
ND
0.15
0.20
ND
0.11
ND
0.12
0.04 U
0.10
ND
ND
ND
ND
ND
ND
U = Under Detection Limit
ND = Not Detected
V = Sample Voided
6of11
1x98.99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Garyville, LA (GALA)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trahs - 1,2 - DICHLOROETHYLENE
1.1 - DICHLOROETHANE
METHYL Urt-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 - DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,} - DICHLOROPROPENE
1.1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
RM>-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m-DICHLOROBENZENE
CHLQROMETHYLBENZENE
p - DICHLOROBENZENE
o - DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-8UTAOIENE
GALA 16752 01
6/6/99
5/26/99
L9EZ008
ppbv
1.13
0.42
1.64
ND
ND
ND
ND
ND
ND
ND
0.31
ND
ND
0.06 U
0.13
ND
ND
ND
0.71
ND
ND
ND
0.04 U
ND
ND
0.28
0/45
0.12
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.83
ND
ND
O.OT 0
1.27
ND
0.14
0.29
ND
0.07 U
ND
0.17
0.06 U
0.14
ND
ND
ND
ND
ND
ND
GALA 15754 02
5/6/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
^ . , v-
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
GALA 15776
5/12/99
5/12/99
L9EZ012
ppbv
0.97
0.55
0.99
1.02
ND
ND
ND
ND
ND
18.69
O.S9
NO
ND
0.12
0.19
NO - » -
ND
0.07
1.24
ND
ND
ND
ND
ND
ND
4.69
0.39
0.10
ND
ND
ND
ND
ND
ND
ND
0.10
ND
ND
1.06
ND
ND
0.12
0.45
ND
0.19
0.36
ND
0.1S
ND
0.19
0.06 U
0.15
ND
ND
ND
ND
ND
ND
GALA 15766
5/18/99
5/26/93
L9EZ013
ppbv
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
NO
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
U = Under Detection limit
NO = Not Detected
V = Sample Voided
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Garyville, LA (GALA)
Yearly Report (September 1998 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHAKE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METH YLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - OICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-OICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1.2- DICHLOROETHANE
1.1,1 • TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1.2 - DICHLOROPROPANE
ETHYL ACRYLATE
8ROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,J - DICHLOROPROPENE
METHYL 1SOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
mj>-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
o-XYLEKE
1,3,5-TRIMETHYLBENZENE
1A4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
o -DICHLOROBENZENE
1,24-TRICHLOROBENZENE
HEXACHLORO-t,3-BUTADIENE
GALA 1681 7
5/30/99
6/9/99
L9FI012
ppbv
1.56
0.66
0.57
132
0.01 U
ND
0.21
ND
ND
0.21
0.29
ND
ND
0.04 U
0.10
ND.
ND
ND
0.53
ND
ND
ND
ND
ND
ND
0.47
0.39
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.54
ND
ND
0.11
ND
ND
0.12
0.28
ND
0.06 U
ND
0.15
0.07 U
0.15
ND
ND
ND
ND
ND
ND
GALA 16856
6/11/99
6/18/99
L9FQ017
ppbv
2.80
1.01
0.67
1.73
0.01 U
ND
0.06
0.02 U
ND
ND
0.32
ND
ND
0.12
0.16
ND -
ND
0.09
0.34
ND
ND
ND
0.06
ND
ND
0.09
0.50
0.10
ND
ND
ND
ND
ND
ND
ND
0.09
ND
ND
0.95
ND
ND
0.09
ND
ND
0.19
0.52
ND
0.09 U
ND
0.27
0.10
0.24
ND
ND
0.02 U
ND
0.01 U
ND
GALA 16985
7/6/99
7/20/89
L9OT013
ppbv
0.59
0.85
0.64
146
ND
ND
0.09
ND
ND
ND
0.31
0.11
ND
0.04 U
0.09
ND
ND
ND
0.31
ND
ND
NO
0.02 U
ND
ND
0.23
0.24
0X19
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.37
ND
ND
0.06 U
ND
ND
0.09 U
0.19
ND
0.04 U
ND
0.11
0.04 U
0.10
ND
ND
ND
ND
ND
ND
GALA 16057
7/17/99
7/28/99
L9G1011
ppbv
1.05
22.73
0.68
1.55
ND
ND
0.21
0.18
ND
ND
0.35
ND
ND
0.11
0.10
ND
ND
0.07
043
0.27
ND
ND
ND
ND
ND
0.13
0.50
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
12.75
ND
ND
0.12
0.03 U
ND
0.23
O.S8
ND
0.10 U
ND
0.28
0.08
0.23
ND
ND
0.03 U
ND
ND
ND
U = Under Detection Unit
ND = Not Detected
Vc Sample Voided
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Garyville, LA (GALA)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
t»hs - 1,2 - OICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-OICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1.2- DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2-DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
OIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1.1,2,2 - TETRACHLOROETHANE
o-XYLENE
1,3,5-TRIMETHYLBENZENE
1.2,4-TRIMETHYtflENZENE
m-DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
GALA 16205
7/29/99
S/11/99
L9HJ016
ppbv
1.00
0.73
0.71
2.12
ND
0.14
0.01 U
O.OS
ND
ND
0.32
ND
ND
0.08 U
0.12
ND
ND
0.06
0.85
ND
ND
ND
0.05
ND
0.30
26.92
0.51
0.11
ND
ND
ND
ND
0.02 U
ND
ND
ND
ND
ND
0.56
ND
ND
0.07 U
ND
ND
0.11
0.26
ND
0.06 U
ND
0.13
0.05 U
0.11
ND
ND
ND
ND
ND
ND
GALA 1634$
8/10/99
8/19/99
L9HQQ21
ppbv
1.75
1.15
0.72
2.59
ND
NO
ND
ND
ND
MO
0.33
ND
0.05
0.07 U
0.11
ND -*-
ND
NO
0.31
ND
ND
ND
0.02 U
ND
ND
0.11
0.38
D.11
ND
ND
ND
ND
ND
ND
ND
ND
ND
NO
0.44
NO
ND
0.07 U
ND
ND
0.10
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Hahnville, LA (HALA)
Yearly Report (September 1998 - September 1999)
SAMPLE SITE # :
SAMPLE DATE
ANALYSIS DATE
PILE MAMS
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-OICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-V-OICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2-DICHLOROETHANE
1,1,4 • TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL tSOBUTYL KETONE
bans • 1,1 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2.2 • TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,24-TRIMETHYLBENZENE
m-DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
D - DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
HALA 16104
9/14/88
10/14/98
L8JM014
ppbv
DM
0.62
0.58
ISO
ND
ND
ND
ND
ND
1,48
0.27
0.76
ND
0.08 U
0.15
ND
ND
ND
0.62
ND
ND
ND
ND
ND
ND
0.07
0.30
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
040
ND
ND
0.07 U
ND
ND
0.08 U
0.20
ND
0.03 U
ND
0.11
O.OS U
0.10
ND
ND
ND
ND
ND
ND
HAU 1$*>1
9/26/98
10/22/98
L8JV007
PPbV
0.66
1.05
0.63
2.64
ND
ND
ND
ND
ND
117.00
042
1.09
ND
0.30
0.30
ND
ND
ND
1.93
ND
ND
ND
ND
ND
ND
0.25
1.16
0.10
ND
ND
ND
ND
ND
ND
ND
0.24
ND
ND
3.06
ND
ND
037
1.95
ND
0.35
0.62
ND
044
ND
0.31
0.07 U
0.24
ND
ND
ND
ND
ND
ND
HALA 15115
10/8/98
10/22/98
L8JV020
Ppbv
240
4.54
0.58
2.1t
ND
ND
0.70
ND
ND
ND
0.25
0.50
ND
0.13
0.13
ND
ND
0.30
0.66
ND
ND
ND
ND
ND
ND
0.05 U
0.70
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.50
ND
ND
0.09 U
ND
ND
0.09 U
0.20
ND
0.06 U
ND
0.10
0.04 U
0.10
ND
ND
ND
ND
ND
MO
HALA 1 61 31
10/14/98
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
U n under Detection limit
ND = Not Detected
V = Voided
1x98.99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Hahnville, LA (HALA)
Yearly Report ( September 1998 - September 1999)
SAMPLE sms*
SAMPLE DATE
ANALYSIS PATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans- V -DICHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL iert<8UTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
CIS-1.2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2-DICHLOROETHANE
1,1,1 • TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMOOICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METH ACRYLATE
cis -1,3 - DICHLOROPROPENE
METHYL 1SOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
D1BROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
o-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBEMZENE
m . DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1.2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTAOIENE
HALA 16169
10/26)98
11/11/98
L8KK019
ppbv
1.96
1.42
0.63
1.J7
ND
ND
1.80
ND
ND
ND
0.27
ND
ND
0.15
0.12
> ND
ND
0.15
0.53
ND
ND
ND
ND
ND
ND
0.08
1.11
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.15
ND
ND
OM
ND
ND
0.37
1.05
ND
0.09 U
ND
OM
0.15
OM
ND
ND
ND
ND
ND
ND
HALA 15179
11/7/98
11/18/98
L8KR009
ppbv
1.54
0.89
0.56
1.37
ND
ND
ND
ND
ND
0.72
0.27
ND
ND
0.13
0.13
*ND
ND
ND
0.54
ND
ND
ND
ND
ND
ND
0.05 U
0.83
0.10
ND
ND
ND
ND
ND
ND
ND
NO
ND
ND
1.10
ND
ND
0.23
ND
ND
030
0.52
ND
0.05 U
ND
0.25
0.09
0.21
ND
ND
ND
ND
ND
ND
HALA 15223
11rt9/98
12/8/98
L8LH007
PPbv
2.03
1.42
0.70
1.62
ND
ND
0.09
ND
ND
ND
0.27
1.36
ND
0.33
0.14
ND
ND
ND
0.68
ND
ND
ND
0.05
ND
ND
0.12
1.20
0.13
ND
ND
ND
ND
0.09
ND
ND
NO
ND
ND
3.27
ND
ND
0.28
0.08 U
ND
0.59
1.54
ND
0.25
ND
0.74
0.24
0.67
ND
ND
0.03 U
ND
ND
ND
HALA 16221
12/1/98
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
U <= Under Detection Limit
ND = Not Detected
V = Voided
TX98.99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Hahnville, LA (HALA)
Yearly Report (September 1998-September 1999)
SAMPLE $(TE#
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - V - DICHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL tBlt-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,2-OICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2-DICHLOROETHANE
1,1,1 - TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1.4 « DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL tSOBUTYL KETONE
trans • 1,3 • OICHLOROPROPENE
1,1,2 . TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1.2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
tn,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
o-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2^-TRIMETHYLBENZENE
m -DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0- DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
HALA 15254
12/13/98
12/91/98
L8LV004
ppbv
1.06
0.69
0.70
1.18
ND
ND
0.04 U
ND
ND
ND
0.29
ND
ND
0.14
0.16
ND
ND
ND
0.76
ND
ND
ND
ND
ND
ND
0.23
0.43
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.54
ND
ND
0.06 U
0.35
ND
0.11
0.21
ND
0.07 U
ND
0.13
0.05 U
0.11
ND
ND
ND
ND
ND
ND
HAW 16292
12/25/98
1/12/99
L9AK018
ppbv
1.60
1.60
0.64
1.03
ND
ND
0.22
ND
ND
0.51
0.28
ND
ND
0.08 U
0.13
ND
ND
ND
1.57
ND
ND
ND
ND
ND
ND
0.07
0.94
0.07 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.56
ND
ND
0.08 U
0.10
ND
0.12
0.2S
ND
0.06 U
ND
0.1S
0.06 U
0.12
ND
ND
ND
ND
ND
ND
HAW 15314
1/9/99
1/21/99
L9AU010
ppbv
1.52
1.44
0.63
1.03
ND
ND
ND
ND
ND
ND
0.03
0.37
ND
ND
0.15
ND
ND
ND
0.96
ND
ND
ND
ND
ND
ND
0.06
0.52
0.07 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
046
ND
ND
0.07 U
ND
ND
0.10
0.19
ND
0.06 U
ND
0.10
0.06 U
0.09
ND
ND
ND
ND
ND
NO
H ALA 1 5391 Df
2/6/99
2/12/99
L9BL013
ppbv
1.28
0.83
0.78
0.89
ND
ND
ND
ND
ND
21.63
042
ND
ND
0.16
0.15
ND
ND
ND
0.58
ND
ND
ND
ND
ND
ND
0.14
0.75
04)7 «
ND
ND
ND
ND
0.05 U
ND
ND
0.06 U
ND
ND
1.20
ND
ND
0.31
0.71
ND
0.29
0.77
ND
0.13
ND
041
0.18
0.56
ND
ND
ND
ND
ND
ND
U - Under Detection Limit
ND = Not Detected
V° Voided
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Hahnville, LA (HALA)
Yearly Report ( September 1998-September 1999)
SAMPLE S|T£#
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLOROD1FLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1.3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans • 1^ -.DICHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL tert-aUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 - DICHLOROETHANE
1.1,1 • TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 -TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
o- DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BLtTADlENE
HAW 15391 R1
276/99
2/17/99
L9BQ009
PPbV
1.09
0.81
0.74
0.86
ND
ND
0.03 U
ND
ND
17.26
0.30
ND
ND
0.21
0.15
ND ., .
ND
ND
0.57
ND
ND
ND
ND
ND
ND
0.16
0.69
0.09
ND
ND
ND
ND
0.05 U
ND
ND
0.05 U
ND
ND
1.13
ND
ND
0.30
0.69
ND
0.28
0.73
ND
0.14
ND
0.38
0.38
0.57
ND
ND
ND
ND
ND
ND
HALA 16393 02
2/5/99
2/12/99
L9BL014
PPbv
1.24
0.82
0.77
0.85
ND
ND
ND
ND
ND
18.05
0.30
ND
ND
0.18
0.14
ND
ND
ND
0.52
ND
ND
ND
ND
ND
ND
0.13
0.69
0.08 U
ND
ND
ND
ND
0.05 U
ND
ND
0.10
ND
ND
1.09
ND
ND
0.79
0.63
ND
0.24
0.61
ND
0.07 U
ND
0.29
0.10
0.26
ND
ND
0.04 U
ND
ND
ND
HALA 16393 R2
2/6/99
2/17/99
L9BQ010
ppbv
1.02
0.80
0.71
0.78
ND
ND
0.04 U
ND
ND
15.80
0.31
ND
ND
0.1S
0.15
ND *.
ND
ND
0.57
ND
ND
ND
NO
ND
ND
0.1S
0.70
0.06 U
ND
ND
ND
ND
0.05 U
ND
ND
0.12
ND
ND
1.15
ND
ND
0.32
0.62
ND
0.23
0.61
ND
0.11
ND
0.31
0.11
0.30
ND
ND
0.04 U
ND
ND
ND
HAU 16416
2/13/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
- V - -
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
U - Under Detection Limit
ND = Not Detected
V = Voided
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Hahnville, LA (HALA)
Yearly Report ( September 1998-September 1999)
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
OICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-OICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
bans - 1,2 - D1CHLOROETHYLENE .
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-V-OICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2- DICHLOROETHANE
1,1,1 • TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL 1SOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 * TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m • DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTAOIENE
HALA1S457
2/23/99
3/10/99
L9CJ011
ppbv
1.07
0.71
0.63
0.97
ND
ND
ND
ND
ND
ND
0.32
0.43
ND
0.06 U
0.11
ND
ND
ND
0.89
1.03
ND
ND
ND
ND
ND
0.05 U
0.44
0.07 U
ND
ND
0.09
ND
ND
ND
ND
0.59
ND
ND
0.50
ND
ND
0.09
ND
ND
0.11
0.27
ND
0.06 - U
ND
0.13
0.09
0.19
0.03 U
ND
0.06 U
0.06 U
0.32
0.13
HALA 15493
3/1/99
3/12/99
L9CL007
ppbv
1.80
1.24
0.60
0.98
ND
ND
0.21
ND
ND
ND
0.28
ND
ND
0.03 U
0.13
ND .
ND
ND
0.75
ND
ND
ND
ND
ND
ND
0.05 U
0.72
0.08
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.88
ND
ND
0.11
0.07 U
ND
0.16
0.43
ND
0.06 U
ND
0.22
0.07 U
0.18
ND
ND
ND
ND
ND
ND
HALA 15491
3/7/99
3/12/99
L8CL009
ppbv
1.31
4.07
0.64
0.79
ND
ND
0.27
ND
ND
0.95
0.28
ND
ND
0.07 U
0.13
,-, ND
ND
ND
0.56
HO
ND
ND
ND
ND
ND
0.07
240
0.07 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
4.99
ND
ND
0.90
0.24
ND
0.17
0.37
ND
0.05 U
ND
0.16
0.06 U
0.15
ND
ND
ND
ND
ND
ND
HALA 15556 D1
3/19/99
4ft2/99
L9DL010
ppbv
3.15
326
0.64
0.91
ND
ND
0.17
ND
ND
3.52
0.30
ND
ND
0.08 U
0.12
ND
ND
4.94
0.58
ND
ND
ND
ND
ND
ND
0.06
0.90
0.07 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.19
ND
ND
0.26
0.04 U
ND
0.22
0.56
ND
0.05 U
ND
027
0.10
0.26
ND
ND
ND
ND
ND
t
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Hahnville, LA (HALA)
Yearly Report ( September 1998 - September 1999)
SAMPLE sire #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
8ROMOMETHANE
CHLOROETHANE
ACETONITRtLE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,2-OICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2-DICHLOROETHANE
1,1,1 • TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1.2 • DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1.3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
mj>-XYLENE
BROMOFORM
STYRENE
1,1,22 -TETRACHLOROETHANE
0 - XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m-DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1,24-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTAD1ENE
HALA 15556 R1
3/19/99
4/13/99
L9DM008
ppbv
341
3.53
0.69
0.94
ND
ND
0.15
ND
ND
3.22
0.33
ND
ND
0.07 U
0.13
ND ,
ND
6.18
0.68
ND
ND
ND
ND
ND
ND
0.07
0.89
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.20
ND
ND
0.29
0.05 U
ND
0.22
0.54
ND
0.05 U
ND
0.28
0.10
026
ND
ND
ND
ND
ND
ND
HALA 15558 02
3/19/99
4/12/39
L9DL011
PPbv
3.22
341
0.72
0.77
ND
ND
0.19
ND
ND
4.73
043
ND
ND
0.09 U
0.12
ND
ND
6.17
0.73
ND
ND
ND
ND
ND
ND
0.08
0.89
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.25
ND
ND
0.33
0.10
ND
0.22
0.61
ND
0.06
ND
0.28
0.11
0.30
ND
ND
ND
ND
ND
ND
HALA 15558 R2
3/1909
4/13/99
L9DM009
ppbv
3.22
3.33
0.69
0.78
ND
ND
0.13
ND
ND
4.03
041
ND
ND
0.09 U
0.13
ND
ND
528
0.77
ND
ND
ND
ND
ND
ND
0.08
0.85
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.28
NO
ND
0.28
0.12
ND
022
0.62
ND
0.04 U
ND
029
0.12
0.29
ND
ND
ND
ND
ND
ND
HALA 15595
3/26/99
4/13/99
L9DL017
PPbV
2.50
0.89
0.68
0.81
ND
ND
ND
ND
ND
ND
0.30
ND
ND
ND
0.09
ND
ND
1.47
ND
ND
ND
ND
ND
ND
ND
0.05 U
0.63
0.06 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.74
ND
ND
0.13
ND
ND
0.18
048
ND
0.05 U
ND
026
0.10
023
ND
ND
ND
ND
ND
ND
U = Under Detection Limit
ND = Not Detected
V = Voided
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Hahnville, LA (HALA)
Yearly Report ( September 1998-September 1999)
$AMPL£$|Te#
SAMPLE DAtE
AHAUVSISDATE
RL6NAME
UNITS
ACETYLENE
PROPYLENE
DICHLOROOIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1.1-OICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans- 1,2 -OICHLOROETHYLENE
1.1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1.2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUm. ETHER
1,2 • DICHLOROETHANE
4,1,1 - TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 • DICHLOROPROPANE
ETHYL ACRYLATE
BROMODJCHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL 1SOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
OIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N4CTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m -DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 'DICHLOROBENZENE
1.24-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
HAtA15$1«
3/31/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
HALA 15680
4/6/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
HALA 15658 01
4/18/99
5/10/9$
L9EJ008
ppbv
1.12
1.73
0.68
1.10
ND
ND
0.37
ND
ND
ND
0.32
ND
ND
0.08 U
0.10
ND
ND
ND
141
1.61
ND
ND
ND
ND
ND
0.07
0.60
0.11
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.81
ND
ND
0.09 U
ND
ND
0.15
0.31
ND
0.05 U
ND
0.17
0.06 U
0.13
ND
ND
ND
ND
ND
ND
HALA 15658 R1
4/18/99
5ft2/99
L9EL007
ppbv
1.22
1.73
0.67
1.08
ND
ND
0.32
ND
ND
ND
0.32
ND
ND
0.08 U
0.10
ND
ND
ND
1.54
1.48
ND
ND
ND
ND
ND
0.07
0.64
0.10
ND
ND
ND
ND
ND
ND
ND
0.10
ND
ND
0.85
ND
ND
0.11
ND
ND
0.15
0.33
ND
0.05 U
ND
0.18
0.07 U
0.13
ND
ND
ND
ND
ND
ND
U = Under Detection Umt
ND = Not Detected
V = Voided
T«S8_99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Hahnville, LA (HALA)
Yearly Report ( September 1998- September 1999)
SAMPLE SITE #
SAMPLE DATE
ANALYSIS PATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 • DICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 • DICHLOROETHANE
1.1,1 • TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METOACRYLATE
cis -1,3 - DICHLOROPROPENE
METHYL 1SOBUTYL KETONE
trans • 1,3 - DICHLOROPROPENE
1,1,2 . TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1.2-DIBROMOETHANE
H-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 -TETRACHLOROETHANE
0-XYLENE
1 ,3.5-TRI M ETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m-DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1,2,4-TRlCHLOROBENZENE
HEXACHLORO-1,3-8UTADIENE
HALA 1 5660 D2
4/18/99
5/10/99
L9EJ009
ppbv
1.10
1.59
0.65
0.96
ND
ND
0.34
ND
ND
ND
0.31
ND
ND
0.07 U
0.09
ND
ND
0.04
1.43
143
ND
ND
ND
ND
ND
0.07
0.57
0.12
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.83
ND
ND
0.08 U
ND
ND
0.14
0.11
ND
0.04 U
ND
0.16
0.06 U
0.11
ND
ND
ND
ND
ND
ND
HALA 16660 JW
4/18/39
$/12/$9
L9EL014
ppbv
1.21
1.63
0.67
0.94
ND
ND
0.29
ND
ND
ND
0.33
ND
ND
0.07 U
0.09
ND - -v
ND
ND
142
1.34
ND
ND
ND
ND
ND
0.07
0.62
0.10
ND
ND
ND
ND
ND
ND
ND
0.07
ND
ND
0.81
ND
ND
0.10
ND
ND
0.13
0.32
ND
0.05 U
ND
0.16
0.05 U
0.13
ND
ND
ND
ND
ND
ND
HALA 15737
4130199
5/18/99
L9ER013
ppbv
1.10
3.79
0.64
1.21
ND
ND
0.13
NO
ND
ND
0.28
ND
ND
0.09 U
0.09
ND
ND
ND
0.86
ND
ND
ND
ND
ND
ND
0.07
0.59
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
5.98
ND
ND
024
ND
ND
0.13
0.31
ND
0.03 U
ND
0.16
0.06 U
0.14
ND
ND
ND
ND
ND
ND
HALA 15762
6/6/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
U o Under Detection Umll
NO - Not Detected
V = Voided
80(11
Tx98 99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Hahnville, LA (HALA)
Yearly Report (September 1998-September 1999)
SAMPLE SITE n
SAMPLE DAte
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1.3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1.1-OICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans • 1.2 - DICHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-OICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 - DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
12 . DICHLOROPROPAHE
ETHYL ACRYLATE
BROMODfCHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1.1 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1.3 - DICHLOROPROPENE
1.1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
ra,p-XYLENE
BROMOFORM
STYRENE
1,1,2.2 - TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m • DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0- DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
H6XACHLORO-1,3-BUTADlENE
HAU 15764
5/6/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
HALA 15769
5/21/99
587/99
L9EZ015
ppbv
1.60
2.46
0.92
0.16
ND
ND
0.27
ND
ND
1.27
0.37
ND
ND
0.07 U
0.10
ND
ND
0.16
1.14
ND
ND
ND
ND
ND
ND
0.06
0.77
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.86
ND
ND
0.11
ND
ND
0.15
0.36
ND
0.05 U
ND
0.18
0.06 U
0.14
ND
ND
ND
ND
ND
ND
HALA 15819
6/30/99
6/9/99
L9FI010
PPPV
2.22
1.36
0.55
1.95
0.01 U
NO
0.08
ND
0.08
0.97
0.27
ND
ND
0.08 U
0.17
ND
ND
0.09
0.64
ND
ND
ND
ND
ND
ND
0.07
0.72
0.11
ND
ND
ND
ND
ND
ND
ND
0.13
ND
ND
0.73
ND
ND
0.18
ND
ND
0.15
0.38
ND
0.07 U
ND
021
0.09
0.21
ND
ND
ND
ND
ND
HO
HALA 15854
6/11/99
6rt8«9
L9FQ016
ppbv
2.23
1.02
0.59
1,75
ND
ND
0.09
0.02 U
ND
ND
0.28
ND
ND
0.08 U
0.11
ND
ND
0.12
0.52
ND
ND
ND
ND
ND
ND
0.09
0.64
0.09 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.13
ND
ND
0.15
0.05 U
ND
0.21
0.55
ND
0.07 U
ND
0.25
0.09
022
ND
ND
0.18
ND
ND
ND
U = Under Detection Umit
ND = Not Detected
V = Voided
TX98.99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Hahnville, LA (HALA)
Yearly Report (September 1998 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHAKE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-OICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - t,2 -OICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-OICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1.2 - DICHLOROETHANE
1,1,1 • TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2-DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-OIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2.2 -TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p- DICHLOROBENZENE
0 - DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORC-1,3-BUTADIENE
HALA 16983
7/5/99
7/20/99
L9GT012
ppbv
0.50
2.08
0.63
4.74
0.01 U
ND
0.10
ND
ND
ND
0.30
ND
ND
0.11
0.11
ND
ND
0.25
0.66
ND
ND
ND
ND
ND
ND
0.06
1.13
0.11
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.55
ND
ND
0.55
ND
ND
0.23
0.63
ND
0.06 U
ND
0.30
0.09
0.21
ND
ND
ND
ND
ND
ND
HALA 16060
7/17/99
7/28/99
L9GI012
ppbv
0.95
1.17
0.75
3.53
ND
ND
0.05 U
ND
ND
ND
1.62
ND
ND
1.37
0.12
ND -
ND
0.10
0.50
ND
ND
ND
ND
ND
ND
0.07
0.59
0.11
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.08
ND
ND
0.15
0.02 U
ND
0.17
0.49
ND
0.06 U
ND
0.24
0.08 U
0.19
ND
ND
0.01 U
ND
ND
ND
HALA 16201
7/29/39
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
HALA 16347
8/10/99
8/19/99
L9HQ022
ppbv
1.15
1.35
0.79
3.SO
ND
ND
0.02 U
ND
ND
ND
0.37
ND
ND
0.09 U
0.13
ND
ND
0.09
1.01
ND
ND
ND
ND
ND
0.21
0.07
0.54
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.57
ND
ND
.0.10
ND
ND
0.15
0.36
ND
0.20
ND
0.20
0.06 U
0.12
ND
ND
ND
ND
ND
ND
U c Under Detection Limit
ND = Not Detected
V-Voided
Tx98_99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Hahnville, LA (HALA)
Yearly Report (September 1998-September 1999)
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHAKE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 • DICHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1.2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-SUTYt ETHER
1,2-DICHLOROETHANE
1,1,1 • TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2- DICHLOROPROPANE
ETHYL ACRYLATE
BROMODiCHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1,3 - DICHLOROPROPENE
METHYL ISOBUTYi KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 . TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-OIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m.p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 -TETRACHLOROETHANE
o-XYLENE
1,3,5-TRIMETHYLBENZENE
1.2,4-TRIMETHYiBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p • DICHLOROBENZENE
g - DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
HALA1644$
8/22/99
9/2/99
L9IB009
ppbv
1.30
1.05
0.63
3.77
NO
ND
0.06
0.03 U
ND
ND
0.32
ND
ND
0.07 U
0.10
ND
ND
ND
0.53
ND
ND
ND
ND
ND
ND
0.07
0.41
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.74
ND
ND
0.12
ND
ND
0.13
0.31
ND
0.08 U
ND
0.16
0.06 U
0.14
ND
ND
ND
ND
ND
ND
HALA teen
9/3/99
9/15/99
L9IN017
PPbv
0.61
1.54
0.58
6.25
ND
ND
ND
ND
ND
ND
0.28
0.15
ND
0.2S
0.10
-ND
ND
ND
0.71
ND
ND
ND
ND
ND
ND
027
0.33
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.48
ND
ND
0.10
ND
ND
0.10
0.26
ND
0.04 U
ND
0.14
0.05 U
0.12
ND
ND
ND
ND
ND
ND
U = Under Detection Limit
ND = Not Detected
V = Voided
1x98.99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - N. Little Rock, AK (PARR)
Yearly Report (September 1998 - March 1999)
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLOROOIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1.1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1.2 - DlCHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,2-DICHLOROETHYLENE
BROMQCHLOROMETHANE
CHLOROFORM
ETHYU tert-BUTYL ETHER
1,2-OICHLOROETHANE
1,1.1 - TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1.2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL MBTHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,13 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
17-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
o-XYLgNe
1,3.5-TRIMETHYLBENZENE
1,2^-TRlMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
o- DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHUORO-1,3-BUTADIENE
PARR 14682
9/3/98
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
PARR 44698
9/8/98
9/25/98
L8IY021/L9AH008
ppbv
1.58
1.57
0.63
1.01
ND
ND
ND
NO
ND
ND
027
ND
ND
04)8 U
0.13
ND
ND
ND
149
ND
ND
ND
ND
ND
ND
OJ17
1.02
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.56
«0
ND
0.07 U
0.09 U
ND
0.11
073
ND
0.05 U
ND
0.14
0.04 U
0.10
ND
NO
ND
ND
ND
ND
PARR 14965
9/20/98
10/14/98
L8JM026
ppbv
1.74
0.99
0.68
1.20
ND
ND
0.05
ND
ND
ND
0.28
NO
ND
0,09 V
0.10
ND - •"
ND
ND
170
ND
ND
ND
0.03 U
ND
ND
0,07
0.66
fl.11
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
143
ND
ND
0.19
ND
ND
0.32
0.85
ND
0.10 U
ND
042
0.12
040
ND
ND
ND
NO
ND
ND
PARR 15106
10/2/98
10722/98
L8JV011
ppbv
1.18
1.16
0.61
148
ND
ND
ND
ND
ND
ND
077
ND
ND
0.95
0.09
ND
ND
ND
0.64
ND
ND
ND
ND
ND
ND
0.06
0.55
0.11
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.91
ND
ND
0.08 U
0.04 U
ND
0.52
0.90
ND
1.65
ND
0.53
0.53
1.77
ND
ND
ND
ND
ND
ND
ND =Not Detected
PARRGREY98.99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - N. Little Rock, AK (PARR)
Yearly Report (September 1998 - March 1999)
U = Under Del*
ND cNot Detected
SAMPLE SITE*
$AMPi£PATE
ANALYSIS DATE
FILE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMCTHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYtONlTRlLE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1£ - DICHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL t«rt-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tart-BUTYL ETHER
12-DICHLOROETHANE
1.1.1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1.2 -DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROM ETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 . DICHLOROPROPENE
METHYL ISOBUTYL KBTONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
12-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROB6NZENE
ETHYLBENZENE
m.p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
o-XYLENE
1.3,5-TRIMETHYLBENZENE
W^-TRIMETrlYLBENZENE
m-DICHLOROBENZENE
CHLOROMETHYLBENZENE
p-DICHLOROBENZENE
o-DICHLOROBENZENB
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
PARR 151 24
10/14/98
11/3/98
L8KC009
ppbv
4.55
2.64
0.90
1.21
ND
ND
0.30
ND
ND
0.15 U
041
ND
ND
0.21
0.13
ND
ND
ND
1.02
ND
ND
ND
ND
ND
ND
0.08
1.26
0.10
ND
ND
ND
ND
ND
ND
ND
0.11
ND
ND
2.53
ND
ND
0.29
0.10
ND
0.57
1.56
ND
021
ND
0.79
0.24
0,73
ND
ND
0.06 U
ND
ND
ND
PARR 16145
10/26/98
11/3/98
L8KC012
PP*>v
5.07
2.16
0.89
1.23
ND
NO
0.25
ND
ND
ts$
0.53
ND
ND
6.85
0.26
' ND ' "
ND
ND
1.23
ND
ND
ND
0.07
ND
ND
am
1.34
0.08 tl
ND
ND
ND
NO
ND
HO
ND
o.<4
ND
ND
322
NO
ND
021
0.08 U
ND
0.63
1.76
ND
0.40
ND
OSS
0.21
0.65
ND
ND
0.06 U
ND
ND
ND
PARR 15185
11/7/98
11/18/38
L8KR012
ppbv
1.56
0.75
0.46
0.62
ND
ND
0.06
ND
ND
ND
0.22
ND
ND
0.07 U
0.08
ND
ND
ND
0.47
ND
ND
ND
ND
ND
ND
0,08
0.49
0.06 U
ND
ND
ND
ND
ND
ND
ND
0.07 U
ND
ND
0.78
ND
ND
0.11
ND
ND
0.18
OM
ND
0,06 U
ND
0.23
0.08
0.23
ND
ND
ND
ND
ND
ND
PARR 16209
11/19/98
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
PARRQREY98.99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - N. Little Rock, AK (PARR)
Yearly Report (September 1998 - March 1999)
U o Under Dele
SAMPLE SITE*
SAMPfcEDATE
ANALYSIS DATE
FILE NAME
UNITS
ACETYLENE
PROPYUENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOM ETHANE
CHLOROETHANE
ACETONITR1LE
TRICHLOROFLUOROMETHANE
ACRYLONITR1LE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tsrt-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
els-V-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 -DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORJDE
tert-AMYL METHYL ETHER
1,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2- TRtCHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANt
TETRACHLOROETHYLENE
CHUOROBENZENE
ETHYLBENZENE
m,p-XYL6NE
BROMOFORM
STYRBN6
1,1,2,2 - TETRACHLOROETHANE
o-XYUENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBBNZeNE
p - DICHLOROBENZENE
o- DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
PARR 16241
12/1/98
12/8/98
L8LH017
ppbv
2.23
1.00
0.60
0.69
ND
ND
0.12
ND
ND
ND
0.27
ND
ND
0.55
0.10
' ND
ND
ND
0.61
ND
ND
ND
ND
ND
ND
0.06
0.65
0.10
ND
ND
ND
ND
ND
ND
ND
ND
NO
ND
1.10
ND
ND
0.12
0.05 U
ND
0.25
O.€0
ND
0.13
ND
0.32
0.10
0.31
ND
NO
ND
ND
ND
ND
PARR 15260
12/13/98
1/8/99
L8AH007
ppbv
1.52
0.51
0.53
0.53
ND
ND
ND
ND
ND
ND
ND
ND
ND
193
0.08
NO
ND
ND
0.52
ND
ND
NO
ND
HO
ND
ND
0.43
0X12 U
ND
ND
ND
ND
ND
NO
ND
NO
ND
ND
047
ND
ND
0.1D
ND
ND
0.13
032
ND
0.07 U
NO
0.14
0.07 U
0.13
ND
ND
ND
NO
ND
ND
PARR 16278
12/25/98
1/12/99
L9AK015
ppbv
2.93
0.88
0.69
0.75
ND
ND
ND
ND
ND
0.72
0.27
NO
ND
0.37
0.11
ND
ND
ND
0.08 U
ND
ND
ND
ND
ND
ND
0.06
0.61
0.10
ND
ND
ND
NO
ND
ND
ND
ND
ND
ND
0.74
ND
ND
0.11
ND
ND
0.19
041
ND
0.06 U
ND
0.24
0.07 U
4.14
ND
ND
ND
ND
ND
ND
PARR 46324
1/6/99
1/21/99
L9AU008
ppbv
3.31
0.83
0.64
0.75
ND
ND
ND
MO
ND
NO
0.32
ND
ND
0.10
0.11
ND
ND
NO
0.62
NO
ND
ND
ND
ND
NO
0.06
0.64
0.09
ND
NO
ND
ND
ND
ND
ND
NO
ND
ND
0.82
ND
ND
0.07
0.11
ND
0.18
043
ND
0.08 U
ND
0.22
0.08
022
ND
ND
ND
ND
ND
ND
ND =Not Detected
V = Vold
PARRGREY98_99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - N. Little Rock, AK (PARR)
Yearly Report (September 1998 - March 1999)
U ° Under Dete
NO =No( Delected
V = Void
SAMPLE SITE #
SAMPUDATC
ANALYSIS DATE
RLE NAME,
UNITS
ACETYLENE
PROPYLENP
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
OICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOM ETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLEN6 CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-U-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
12 - DICHLOROETHANE
1,1,1 - TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
W -DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL MBTHA$RYtAT$
els -1,3 - DICHLOROPROPENE
METHYL (SO$UTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2-TRtCHLaROrrHANE
TOLUENE
PIBR0MOCM10ROMETHANE
12-OIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROB6NZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1.12.2 • TETRACHLOROETHANE
o-XYLENE
1,3,5-TRIMETHYLBENZENE
1^,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p- DICHLOROBENZENE
o- DICHLOROBENZENE
1.2ATRICHLOROBENZENE
HEXACHLORO*1,3-BUTADIENE
PARR 16362
1/18/99
2/2/99
L9BB008
ppbv
2.22
1.16
0.88
0.66
ND
ND
0.11
ND
ND
1.02
029
ND
ND
4.78
0.15
ND
ND
NO
0.66
ND
ND
ND
0.06
ND
ND
0.09
0.68
0,08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.11
ND
ND
0.12
ND
NO
0.24
0.58
ND
0,15
ND
4.31
0.13
0.31
ND
ND
ND
ND
ND
ND
PARR 18972
1/30/99
2/11/99
L9BJ009
ppbv
1.88
0,82
0.63
0.72
ND
No
ND
ND
ND
ND
029
NO
ND
2.99
0.14
NO "
ND
ND
0.66
ND
ND
NO
0.04 U
NO
NO
0.07
0.58
0.08 U
ND
ND
ND
ND
ND
ND
ND
0.07
ND
NO
0.81
HO
ND
0,08 U
ND
NO
0.18
0.41
ND
P.11 U
ND
0.26
0.10
023
ND
NO
ND
HO
ND
ND
PARR 16399
2/11/99
2/17/99
L9BQ011
ppbv
0.65
0.29
0.60
0.75
ND
ND
0.20
NO
ND
ND
028
ND
ND
0.05 U
0.08
ND
ND
NO
0.32
NO
ND
ND
ND
ND
ND
0,07
026
0.08 U
ND
NO
ND
ND
ND
ND
ND
0.06 U
ND
NO
0.31
NO
ND
0.04 U
ND
NO
0.09 U
0.18
ND
0,06 U
ND
0,10
0.05 U
0.11
ND
ND
ND
NO
ND
ND
PARR 16431
2/17/99;
2/24/99
L9BW014
ppbv
1.68
0.51
0.64
0.63
ND
ND
ND
ND
ND
NO
029
NO
ND
0.27
0.10
NO
ND
NO
0.92
ND
ND
ND
ND
ND
ND
0.06
0.44
0.08 U
ND
HO
ND
NO
ND
HO
ND
ND
ND
ND
0.58
NO
ND
0.07 V
0.05 U
ND
0.13
0.32
ND
0.06 U
ND
0.17
0.06 U
0,17
ND
NO
ND
ND
ND
ND
4o(7
PARRGREY96_99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - N. Little Rock, AK (PARR)
Yearly Report (September 1998 - March 1999)
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYUNE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-OICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans- 1,2 -OICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLpROPRENE
cls-1.2-OICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL teit-SUTYL ETHER
1,2 - DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2* DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANB
TETRACHLOROETHYLENE
CHLOROBEN2ENE
ETHYLBENZENE
m.p-XYLENE
BROMOFORM
STYRENB
1,1,2,2 - TETRACHLOROETHANE
o-XYLENE
1,3.5-TRIMETHYLBENZENE
1,24-TRIMETHYLSENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
o - DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
PARR 15461
2S3/99
3/10/99
L9CJ01Q
ppbv
2.54
0.81
0.62
0.61
ND
ND
ND
ND
ND
ND
0.30
ND
ND
0.18
0.09
ND
ND
ND
0.93
ND
ND
ND
ND
ND
ND
0.06
0.57
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
NO
0.77
ND
ND
0.08
ND
ND
0.19
0.48
ND
0,04 U
ND
0.26
0.09
0.23
ND
ND
ND
ND
ND
ND
I>ARR16S1$
3/1/99
$/1 7/99
L9CQ006
ppbv
3.15
1,22
0.62
0.56
ND
ND
0.13
ND
ND
ND
0.26
ND
ND
0.34
0.09
ND -**
ND
ND
0.67
ND
ND
ND
ND
ND
ND
0.06
0.86
0.07 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.56
ND
ND
0.12
0.04 U
ND
0.31
0.88
ND
0.10 U
ND
043
0.16
0.44
ND
ND
0.03 U
ND
ND
ND
PARRl660f
3/7/99
3/17/99
L9CQ008
ppbv
0.83
0,32
0.56
0.64
ND
ND
ND
ND
ND
ND
0.27
NO
ND
O.D6 U
0.09
ND
ND
ND
041
ND
ND
ND
ND
ND
ND
0.04 U
028
0.04 U
ND
ND
ND
ND
ND
ND
ND
NO
ND
ND
0.26
ND
ND
0.03 U
ND
NO
0.08 U
0.14
ND
0.05 U
ND
0.08
0.05 U
0.10
ND
NO
ND
NO
ND
ND
PARR 1 6697 D1
3/17/99
4/12/99
L9DL008
ppfav
146
0.56
0.61
0.59
ND
ND
ND
ND
ND
NO
0.29
ND
ND
0.13
0.09
ND
ND
ND
048
ND
ND
ND
ND
NO
ND
0.05 U
040
0.0$ V
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.54
ND
ND
0.06 U
0.06 U
ND
0.12
O.J1
ND
0.07 U
ND
0.14
0.08
0.17
ND
ND
ND
NO
ND
ND
ND =Not Detected
V = Void
5 o!7
PARRGREY98.99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - N. Little Rock, AK (PARR)
Yearly Report (September 1998 - March 1999)
SAMPteslTE*
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONlTlHLE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETH YLENE
1,1 • DICHLOROETHANE
METHYL t*rt-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL fert-BUT YL ETHER
1,2 - DICHLOROETHANE
1,1,1 • TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
W - DICHLOROPROPANH
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL taetHACRYLATe
els -1,3 - DICHLOROPROPENE
METHYL JSOBUT YL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 * TRICHLOROETHANE
TOLUENE
D1BROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
o-XYLENE
1,3,5-TRIMETHYLBENZENE
1A4-TftlMETHYLeENZENB
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
o- DICHLOROBENZENE
1,24-TRICHLOROBENZENE
HEXACHLpRO-I.J-BUTADIENE
PARR 15697 R1
3/17/99
4/13/99
L9DM006
ppbv
1.18
0.56
0.64
0.64
ND
ND
ND
ND
ND
ND
0.29
ND
ND
0.12
0.08
ND
ND
ND
0.48
ND
ND
NO
ND
ND
ND
0.06
043
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.55
ND
ND
0.05 U
0.06 U
ND
0.12
0.30
ND
0.08 U
ND
0.17
0.06 U
0.16
ND
ND
ND
ND
ND
ND
PARR 1 $59902
3/17/99
4/12/99
L9DL009
ppbv
1.54
0.5?
0.67
0.71
ND
MO
ND
ND
ND
ND
0.29
NO
ND
fl.11
0.08
ND
ND
NO
0.45
ND
ND
NO
ND
ND
ND
0,05 U
042
0.09 U
ND
ND
ND
NO
ND
ND
ND
HO
NO
NO
0.54
ND
ND
0.06 U
0.05 U
NO
0.13
029
ND
0.07 U
ND
0,16
0.06 U
0.16
ND
ND
ND
NO
ND
ND
PARR 1 5699 R2
3/17/9$
4/13/99
L9DM007
ppbv
1.35
. 0.59
0.68
0.72
ND
ND
ND
ND
ND
ND
0.35
ND
ND
0.10
0.10
ND
ND
ND
047
ND
ND
ND
ND
ND
ND
0.05 U
043
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.58
ND
ND
0.06 U
0.07 U
ND
0.12
0.30
ND
0.06 U
ND
0.15
0.06 U
0.15
ND
ND
ND
ND
ND
ND
PARR 16684
3/25/99
4/13/99
L9DL014
ppbv
1.27
0.54
0.62
0.71
ND
ND
ND
ND
ND
ND
0.32
ND
ND
0.18
0.09
ND
ND
ND
1.00
ND
ND
ND
ND
NO
ND
0.05 U
0.36
0.08 U
ND
NO
ND
ND
ND
ND
ND
ND
ND
ND
040
ND
ND
0.09 U
ND
ND
0.12
0.25
ND
0.05 U
ND
0.14
0.07 U
0.16
ND
ND
ND
ND
ND
ND
ND-Not Detected
VnVOlli
6of7
PARRGREY98.99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - N. Little Rock, AK (PARR)
Yearly Report (September 1998 - March 1999)
U = Under Detection Umit
NO =Not Detected
V = Vold
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
RLE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRlLE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE—
1,1-DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,Z-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2-DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 • DICHLOROPROPENE
1,1,2 -TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1.2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
V.4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYUBENZENE
p - DICHLOROBENZENE
0- DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1,J-BUTADIENE
PARR 1 S614
3/31/99
4/22/99
L9DU012
PPbV
1.33
0.86
0.59
0.?8
ND
NO
ND
ND
ND
ND
0.29
ND
ND
0.13
0.08
" ND
ND
ND
0.66
ND
ND
ND
ND
ND
ND
0.05 U
045
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.57
ND
ND
0,04 U
0.02 U
ND
0.14
0.33
ND
0,10 U
ND
0.18
0.08
0.19
ND
ND
ND
ND
ND
ND
PARRGREY98.99
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Rutland, VT (RUVT)
Yearly Report (September 1998 - September 1999 )
SAMPtESJtE*
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLOROOIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETPNITWLE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYU5NE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETH YLENE
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1 ,2-DlCHLOROETH YLENE
BROMOCHLQRDMETHANE
CHLOROFORM
ETHYL terf-BUTYL ETHER
1 .2 - DICHLOROETHANE
1,1,1 • TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1 X' DKJHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - OICHLOROPROPENE
1 ,1 3 • TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m.P-*YLeNE
BROMOFORM
STYRENE
1 ,1 ,2,2 - TETRACHLOROETHANE
o - XYLENE
1,3,5-TRIMETHYLBENZENE
1 ,2>TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLORQMEfHYLBENZENE
p. DICHLOROBENZENE
0- DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
RUVt 14690
9/2/98
9/25/98
L8IY019
ppbv
2.22
1,02
0.94
0.62
ND
ND
0.09
ND
ND
ND
0.67
ND
ND
ND
0.04
ND
ND
0.43
0.69
ND
ND
ND
ND
ND
ND
0.07
0.64
0.12
ND
ND
ND
ND
ND
ND
ND
NO
ND
ND
1.96
NO
ND
NP
ND
ND
0.33
0.82
ND
ND
ND
Q.44
0.07 U
0.27
ND
ND
ND
ND
ND
ND
RUVTUBZt
9/14798
10/14/98
L8JM010
ppbv
2.45
1.32
0.80
0.72
ND
ND
0.14
ND
ND
ND
0.35
ND
ND
0,23
0.09
ND
ND
0.55
1.08
ND
ND
ND
0.03 U
ND
ND
0.08
0.82
0.11
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.71
ND
ND
0.07 t)
0.05 U
ND
0.36
1,01
ND
0.10
ND
0.49
0.15
0.44
ND
ND
ND
ND
ND
ND
RUVT t49?$
9/20/98
10/14/98
L8JM028
ppbv
1.66
0,91
0.71
0.62
ND
ND
0.08
ND
ND
ND
0.32
ND
ND
0.16
0.10
ND
ND
0,42
0.69
ND
ND
ND
0.01 U
ND
ND
0.09
0.73
0.11
ND
ND
ND
NO
ND
ND
ND
ND
ND
ND
2.15
NO
ND
0.08 U
0.02 U
ND
0.31
0.78
ND
0.10
ND
0.4D
0.11
0.38
ND
ND
ND
ND
ND
ND
RUVT 16060
9/2608
10/22/98
L8JV006
ppbv
1.94
1.06
0.63
0.46
ND
ND • '
0.12
ND
NO
0.91
0.24
ND
ND
0.14
0.05
ND-
ND
0.47
0.52
ND
ND
ND
ND
ND
ND
0.06 : .
0.97
0.08 . U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
4.71
ND
ND
0.20
ND
ND
0.37
1.15
ND
0.05 U
ND
0.55
0.19
0.68
ND
NO
ND
ND
ND
ND
U = Under Detection Umll
ND = Not Detected
V = Voided
1of11
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Rutland, VT (RUVT)
Yearly Report ( September 1998 - September 1999 )
SAMPU6SITE*
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VfNYL CHLORIDE
1,3-BUTADIENE
BROMOM ETHANE
CHLOROETHANE
ACETOWTRILE
TRICHLOROFLUOROMETHANE
ACRYLONITR1LE
1 ,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans'. 1,2 - DICHLOROETH YLENE
1,1 -DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1 ,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2- DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 • PICHLDROPROPANE
ETHYL ACRYLATE
BRDMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1 ,3 - DICHLOROPROPENE
METHYL ISOBOTYL KETONE
trans - 1.3 - DICHLOROPROPENE
1 ,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m.p - XYLENE
BROMOFORM
STYRENE
1 ,1 ,2,2 - TETRACHLOROETHANE
o - XYLENE
1,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIMETH YLflENZENE
m - DICHLOROBENZENE
CHLOROM ETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
RUVM6111
10/8/98
10/22/98
L8JV017
ppbv
1.86
1,04
0.61
0.44
ND
ND
0.07
ND
ND
1,25
0.30
ND
ND
0.33
0.09
ND--
ND
0.55
0.36
ND
ND
ND
ND
ND
ND
0.06
1.08
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.60
ND
ND
0.12
ND
ND
0.38
1.13
ND
0.08 U
ND
0.51
0.13
0.65
ND
ND
ND
ND
ND
ND
RUVT 161 36
10/20/98
12/6/98
L8LFOOT
ppbv
1.59
O.S7
0.56
0.54
ND
ND
0.03 U
ND
ND
1.51
0.29
ND
ND
0.07 U
0.10
ND
ND
0.17
0.78
ND
ND
ND
ND
ND
ND
0.07
0.55
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.12
ND
ND
0.11
ND
ND
0.18
0.49
ND
0.06 U
ND
0.26
0.10
0.29
ND
ND
ND
ND
ND
ND
RUVT 16167
11/1/98
11/18/98
L8KR006
ppbv
0.97
0,49
0.48
O.S1
ND
ND
0.03 U
ND
ND
0.03 U
0.25
ND
ND
0.03 U
0.08
~- ND
ND
ND
0.35
ND
ND
ND
ND
ND
ND
0.05 U
0.39
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.57
ND
ND
0.05 U
ND
ND
0.11
0.27
ND
0.06 U
ND
0,14
0.06 U
0.14
ND
ND
ND
ND
ND
ND
RUVT 16201
11/13/98
12/1/98
L8LA012
ppbv
2.89
1.08
0.61
0.57
ND
ND
0.15
ND
ND
0.85
0.28
ND
ND
0.05 U
0.10
ND '-"
ND
0.19
0.46
ND
ND
ND
ND
ND
ND
0.07
0.79
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.68
ND
ND
0.11
ND
ND
0.26
0.75
ND
0.06 U
ND
0.35
0.13
0.33
ND
ND
ND
NO
ND
ND
U = Under Detection Unit
ND = Not Delected
V-Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Rutland, VT (RUVT)
Yearly Report (September 1998 - September 1999 )
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
FILENAME ,
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETQNITRlii
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 • DICHLOROETHYLENE
1.1 -DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1 ,2-OICHLOROETHYLENE
BROMOCHLORDMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1.2 -DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - DICHLORPPRDPANE
ETHYL ACRYLATE
BROMOOICHLOROMETHANE
TRICHLOROETHYLENE
METHYL WETHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1 ,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROM ETHANE
1,2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-*YLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
o - XYLENE
1 ,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
RUVT +6229
11/26/98
12/8/09
L8LH011
ppbv
2.35
0.97
0.60
0.55
ND
NP
0.03 U
ND
ND
ND
0.27
ND
ND
0.03 U
0.09
ND
ND
0,19
0.30
ND
ND
NO
ND
ND
ND
0.07
0.78
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
NO
1.38
ND
ND
0.07 U
ND
ND
0.22
0.60
ND
0.06 U
ND
0,30
0.11
0.28
ND
ND
ND
ND
ND
ND
RUVT 16246
12/7/98
12/31/98
L8LV006
ppbv
1.21
0.65
0.63
0.62
ND
ND
ND
ND
ND
2.31
0.29
ND
ND
0.08 U
0.09
ND
ND
0.13
0.36
ND
ND
ND
ND
ND
ND
0.07
0.39
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
o.eo
ND
ND
0.08 U
ND
ND
0.14
0.3B
ND
0.05 U
ND
0.21
0.06 U
0.18
ND
ND
ND
ND
ND
ND
RUVT 16260
12/19/98
1/12/99
L9AK009
ppbv
5.86
2.50
0.71
0.61
ND
ND
0.34
ND
ND
ND
0.43
ND
ND
0.19
0.09
ND
ND
0.43
0.58
ND
ND
NO
ND
ND
ND
0,05 U
1.52
0.09
ND
"ND
ND
ND
ND
ND
ND
ND
ND
ND
2.84
ND
ND
0.1 B
ND
ND
0.47
1.40
ND
0.13
ND
0.69
0.19
0.55
ND
ND
ND
ND
ND
ND
RUVT 16306
12/31/88
1/12/99
WAK021 ,
ppbv
5.09
2.01
0.75
0.61
ND
ND
0.30
ND
ND
NO
0.29
ND
ND
0.86
0.09
¥D
ND
0.22
0.50
ND
ND
ND
ND
NO
ND
0.05 U
1.31
O.OT U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.42
NO
ND
0.10
ND
ND
0.46
1426
ND
0.10 U
ND
0.65
0.17
0.48
ND
ND
ND
ND
ND
ND
U <= Under Detection Unit
ND = Not Detected
V = Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Rutland, VT (RUVT)
Yearly Report (September 1998 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYL6NE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1,1 -DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1 ,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2- DICHLOROETHANE
1,1.1 • TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2- DICHLQROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1 ,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 -TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OOTANE
TETRACHLOROETHYLENE
CHLOROBENZEN6
ETHYLBENZENE
m.p • XYLENE
BROMOFORM
STYRENE
1 ,1 ,2,2 - TETRACHLOROETHANE
o - XYLENE
1 ,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIMETH YLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
RUVT 15320
1/12/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
RUVT 16346 O1
1/24/99
2/2/99
L9BB009
ppbv
2.84
1.43
0.66
0.67
ND
ND
0.22
ND
ND
0.41
0.31
ND
ND
0.09 U
0.09
ND
ND
0.42
0.30
ND
ND
ND
ND
ND
ND
0.06
0.98
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.41
ND
ND
0.16
ND
ND
0.48
1.51
ND
0.10 U
ND
0.72
0.27
0.76
ND
ND
ND
ND
ND
ND
ftOVT1S*tSR1
1/24/99
2/9/99
L9BIOOS
ppbv
2.90
1,47
0.68
0.66
ND
ND
0.22
ND
ND
0.4B
0.32
ND
ND
0.13
0.09
ND
ND
'0.43
0.36
ND
ND
ND
ND
ND
ND
0,05 U
0.93
0X19
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.39
ND
ND
0.16
ND
ND
0.47
1.44
ND
0.09 U
ND
0.72
0.25
0.74
ND
ND
ND
NO
ND
ND
RUVT1$M7D2
1/24/99
2/2/99
L9BB010
ppbv
2.82
1.34
0.70
0.60
ND
ND
0.16
ND
ND
2.73
0.30
ND
ND
0,07 U
0.09
• NO- ^~" - •
ND
0.41
o.i e
ND
ND
ND
ND
ND
ND
0.04 U
0.97
0.08 V
ND
ND
ND
ND
ND
ND
ND
NO
ND
ND
2.50
ND
ND
O.t6
ND
ND
0.49
1.49
ND
0X19 U
ND
0.77
0.27
0.75
ND
ND
ND
ND
ND
ND
U = Under Detection Limit
NO - Not Detected
V = Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Rutland, VT (RUVT)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITES
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROM ETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITR1LE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1 ,2-DICHLOROETH YLENE
BROMOCHLORDMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 - DICHLOROETHANE
1.1,1 - TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1 2- D1CHLDROPRDPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
M6THYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1 ,1,2 - TRICHLOROETHANE
TOLUENE
DIBKOMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p - XYLENE
BROMOFORM
STYRENE
1 ,1 ,2,2 - TETRACHLOROETHANE
o - XYLENE
1,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADtENE
RUVf 16347 R2
1/24/99
2/9/99
198,1006
ppbv
2.81
1JB
0.64
0.60
ND
NO
0.20
ND
ND
2.06
0.29
ND
ND
0.07 U
0.09
ND
ND
0,42
0.19
ND
ND
ND
ND
ND
ND
Q.05 U
0.94
0.05 U
ND
ND
ND
ND
ND
ND
ND
NO
ND
ND
2.39
ND
ND
0-15
ND
ND
0.47
1.4S
ND
0.11
ND
0.74
0.27
0.77
ND
ND
ND
ND
ND
ND
RUVT 16409
2/6/99
2/23/99
L9BW008
ppbv
1.62
0.70
0.62
0.57
ND
ND
0.04 U
NO
ND
1.15
0.29
NO
ND
0.07 U
0.09
ND
ND
0.13
0.33
ND
ND
ND
ND
ND
ND
D.06
0.55
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.06
ND
ND
0.07 U
ND
ND
0.22
0.59
ND
0.04 U
ND
0.31
0.10
026
ND
ND
ND
NO
ND
ND
RUVT 15445
2/17/99
3/4/99
L9CD012
ppbv
2.04
OJS
0.59
0,60
ND
•ND
0.09
ND
ND
0,46
0.42
ND
ND
0.10
0.08
ND
ND
0.19
0.53
ND
ND
ND
ND
NO
ND
0,06
' 0.62
0X16 U
ND
ND
ND
NO
ND
ND
ND
ND
ND
NO
0.93
ND
ND
ND
0.02 U
ND
0.14
0.43
ND
0.02 U
ND
0.20
0.05 U
0.14
ND
ND
ND
•ND
ND
ND
RUVT 16479
3/1/99
3/11/99
L9CJ021
ppbv
2.86
1.10
0.62
0.60
ND
ND
0.11
ND
ND
0.63
0.28
ND
ND
O.OB U
0.03
ND
ND
0.28
0.42
ND
ND
NO
ND
ND
ND
0.05 U
0.73
O.OS U
0.06
ND
ND
ND
ND
ND
ND
ND
ND
NO
1.19
ND
ND
0.10
ND
NO
0.23
0.61
ND
0.05 U
ND
0.31
0.10
0.29
ND
NO
ND
ND
ND
ND
U = Under Detection Umit
ND = Not Delected
V « Voided
\A98_e9
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) • Rutland, VT (RUVT)
Yearly Report ( September 1998 - September 1999 )
SAMPtESITE*
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOM ETHANE
CHLOROETHANE
ACETONITRU.E
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYiENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans • 1,2-OICHLOROETHYLENE
1,1 - OICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1 ,2-DICHLOROETHYLENE
BROMOCHLDROM ETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1.2 -OICHLOROETHANE
1.1.1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2- DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - OICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1 ,1 ,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROM ETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBEN2ENE
ETHYLBENZENE
m,p-XYL£NE
BROMOFORM
STYRENE
1 ,1 ,2,2 - TETRACHLOROETHANE
p • XYLENE
1,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIMETHYLBENZENE
m - OICHLOROBENZENE
CHLOROMETWYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
RUVT 1S650
3/13/99
3/24/99
L9CX01S
ppbv
1.40
0,58
0.63
0.64
ND
NO
0.03 U
ND
ND
ND
0.28
ND
ND
ND
0.09
ND
ND
ND
0.28
ND
ND
NO
ND
ND
ND
0,07
0.49
0.06 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.49
ND
ND
ND
ND
ND
0.10
0.25
ND
0.02 U
ND
0,13
0.04 U
0X18 U
ND
NO
ND
ND
ND
ND
RUVT 16666
3/19/99
4/12/99
L9DL013
ppbv
0.74
0.65
0.64
0.63
ND
ND
ND
ND
ND
ND
0.42
ND
ND
0.06 U
0.09
ND
ND
0.12
0.74
ND
ND
ND
ND
ND
ND
0.05 U
0.42
0.07 U
ND
ND
ND
ND
ND
NO
ND
ND
ND
ND
0.51
ND
ND
ND
ND
ND
0.12
0.28
ND
0X13 U
ND
0.15
0.05 U
0.12
ND
ND
ND
ND
ND
ND
RUVT 15628 D1
3/25/99
4/21/99
L9DU007
ppbv
1.20
0,46
0.60
0.60
ND
ND
ND
ND
ND
0.3E
0.31
NO
ND
0.21
0.09
ND
ND
0.13
.1.66
ND
ND
ND
ND
ND
ND
0.04 U
0.36
0X15 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
NO
0.46
ND
ND
0.03 U
ND
ND
0.10
0.27
ND
0.06 U
ND
0.15
0.07 U
0.11
ND
ND
ND
ND
ND
ND
RUVT 16628 R1
3/26/99
5/7/99
L9ED030
ppbv
1.17
0.32
0.62
0.62
ND
NO
0.02 U
ND
ND
NO
0.41
NO
ND
0.22
0.09
ND
ND
0.10
2.06
ND
ND
ND
ND
NO
ND
0.06
0.36
0.03 U
ND
NO
ND
NO
ND
ND
ND
ND
ND
ND
0.48
ND
ND
0.05 U
ND
ND
0.11
0.23
ND
0.03 U
ND
0.13
0.04 U
0.10
ND
ND
ND
ND
ND
ND
U = Under Detection Limit
ND = Not Detected
V = Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Rutland, VT (RUVT)
Yearly Report (September 1998 - September 1999 )
$AMPLES)T6#
SAMPLE DATE
ANALYSIS DATE
RLE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRftE
TRICHLOROFLUOROMETHANE
ACRYLONITR1LE
1,1-DICHLOROETHENE
METH YLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETH YLENE
1,1 - DICHLOROETHANE
METHYL t«rt-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
els-1 ,2-DICHLOROETH YLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tetl-BUTYL ETHER
1,2 - DICHLOROETHANE
1.1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1 2 • D1CHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISQBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1 ,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROM ETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p - XYLENE
BROMOFORM
STYRENE
1,1,2,2-TETRACHLOROETHANE
o - XYLENE
1,3,6-TRIMETHYLBENZENE
1 ^ A-TRIMETHYL6ENZENE
m - DICHLOROBENZENE
CHLORQMETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
RUVt 16530 D2
3/25/99
4/21/99
L9DU008
ppbv
1.15
0.40
0.59
0.68
ND
ND
ND
ND
ND
2.27
0.51
ND
ND
0.26
0.09
ND
ND
0.10
O.E5
ND
ND
ND
ND
ND
ND
0.06
0.36
0.07 a
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.45
ND
ND
0.05 U
ND
NO
0.11
0.24
ND
O.OS XI
ND
0.14
0.06 U
0.12
ND
ND
ND
ND
ND
ND
R.l)VT1«630fcZ.
3/26/99
4/22/99
L9DV004
ppbv
1.27
0.44
0.64
0.60
ND
ND
ND
ND
ND
2.34
0.52
ND
ND
0,24
ND
ND
ND
ND
0.72
ND
ND
ND
ND
ND
ND
0.05 tl
0.36
0.08 XI
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.47
ND
ND
O.OS U
ND
ND
0.10
0.24
ND
0.03 U
ND
0.14
0.05 U
0.10
ND
NO
ND
ND
ND
ND
RUVT 15632
4/6/99
4/22/99
L9DV009
ppbv
2.50
1.44
0.68
0.68
ND
ND
0.14
ND
ND
ND
0.34
ND
ND
0.26
0.10
ND
ND
0.3D
0.66
ND
ND
ND
ND
ND
ND
0.06
0.73
0.07 U
ND
NO
ND
ND
ND
ND
ND
ND
ND
ND
2.08
ND
ND
0.13
0.02 U
ND
0.28
0.76
ND
0.06 XI
ND
0.35
0.13
043
ND
ND
ND
ND
ND
ND
RUW 16678
4/18/99
6/11/99
L9EJ014
ppbv
5.36
0.60
0.67
0.74
ND
ND
0.05
ND
ND
NO
0.44
ND
ND
0.09 U
0.08
ND "•"•" ' '
ND
0.16
0.59
ND
ND
ND
ND
ND
ND
0.06
0.44
0.09 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.97
ND
ND
0.11
ND
ND
0.33
0.68
ND
0.37
ND
0.40
0.39
0.97
ND
ND
ND
ND
ND
ND
U = Under Detection Unit
ND = Not Detected
V = Voided
vige.gg
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Rutland, VT (RUVT)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SffE#
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1.3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITR1LE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2- DICHLOROETHYLBIE
1,1 -OICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1 ,2-DICHLOROETHYLENE
BROMOCHLORDMETHANE
CHLOROFORM
ETHYL «ert-8UTYL ETHER
1,2-DICHLOROETHANE
1.1,1 -TRIQHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2- DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 • DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1 ,3 - DICHLOROPROPENE
1 ,1 .2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1.2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p - XYLENE
BROMOFORM
STYRENE
1 ,1 ,2,2 - TETRACHLOROETHANE
o - XYLENE
1,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIMETHYtBENZENE
m • DICHLOROBENZENE
CHLOROM ETHYLBENZENE
p - DICHLOROBENZENE
0- DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
RUVT 16731
4/30/99
5/18/99
L9ER011
ppbv
2.36
1.13
0.73
0.68
ND
ND
0.13
ND
ND
ND
0.33
ND
ND
0.46
0.10
ND
ND
0.39
0.66
ND
ND
ND
ND
ND
ND
0.08
0.79
,0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.89
ND
ND
0.1 5
ND
ND
0.30
0.89
ND
0.07 U
ND
0.44
0.14
0.40
ND
ND
ND
ND
ND
ND
RUVt 16822
6/12/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
RUVT 16824
6/12/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
RUVT 16784
6/24/99
6/7/99
L9FG012
ppbv
1.40
0.71
0.74
0.69
0.01 U
ND
0.07
NO
ND
20.43
0.40
ND
ND
0.16
0.10
ND
ND
0.18
1.36
ND
ND
ND
ND
ND
ND
0.08
0.40
0.10
ND
ND
ND
NO
ND
ND
ND
0.09
ND
ND
1.13
ND
ND
0.11
O.OS U
NO
0.20
0.46
ND
0.11 U
ND
0.23
0.08
0.19
ND
ND
0.01 U
ND
ND
NO
U = Under Detection Limit
NO * Not Detected
V = Voided
M98.99
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Rutland, VT (RUVT)
Yearly Report (September 1998 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETMANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRItE
1,1-DICHLOROETHENE
METHYUENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans • 1,2 - DICHLOROETHYLENE
1.1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1 ,2-DICHLOROETH YLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 -DICHLOROETHANE
1.1,1 - TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2- DICHLORDPRDPANE
ETHYL ACRYLATE
BROMODICHLOROM ETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBOTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 -TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p -JCYLENE
BROMOFORM
STYRENE
1 ,1 ,2,2 - TETRACHLOROETHANE
o - XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-T«IMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p • DICHLOROBENZENE
0 .DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
RUVT 16904
6/5/99
6/24/93
L9FW010
ppbv
2.43
0,78
0.62
0.64
0.01 U
ND
0.09
0.02 U
ND
2X1
0.30
ND
ND
0.13
0.11
ND
ND
0,27
0.62
ND
ND
ND
0.03 U
ND
ND
O.OB
O.S2
0X19
0.02 U
ND
ND
ND
ND
ND
ND
ND
ND
NO
1.53
ND
ND
0.15
0.02 U
ND
0.35
0.9G
ND
0.08 U
ND
0.4B
0.16
0.41
ND
ND
0.02 U
ND
ND
ND
RUVT16926
6/17/99
ppbtf
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
RUVT 1602$
6/29/99
7/20/99
L9GT009
ppbv
1.70
1,02
1.40
0.87
ND
ND
0.12
0.04
ND
1,20
0.31
ND
ND
0.13
0.10
ND
ND
0.43
1.07
ND
ND
ND
ND
ND
ND
0.06
0.60
0.09
ND
ND
ND
ND
0.02 U
'ND
ND
0.14
ND
ND
3.83
ND
ND
0.20
0.05 U
ND
0.40
0.85
ND
0.26
ND
0.42
0.14
0.39
ND
NO
0.03 U
ND
ND
ND
RUVT 1626B
7/17/99
8/10/99
L9HJ012
ppbv
1.42
0.77
0.81
0.76
ND
ND
0.05 U
0.03 U
ND
ND ' •'
0.39
ND
ND
0,11 !
0.12
ND
ND
0.28
0.96
ND
ND
ND
ND
NO
ND
0.08
0.56
0.11
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.46
ND
ND
0.11
ND
ND
0.24
0.66
ND
0.07 U
ND
0.31
0.10
0.26
ND
ND
0.02 U
ND
ND
ND
U = Under Detection Limit
ND = Not Detected
V = Voided
vtae.M
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Rutland, VT (RUVT)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPVLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROM ETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METH YLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1 ,2-DICHLOROETHYLENE
8ROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2- DICHLOROETHANE
1,1,1 • TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2- DICHLDROPROPANE
ETHYL ACRYLATE
BROMOD1CHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1,3 • DICHLOROPROPENE
METHYL ISOBOTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1 ,1 ,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
NOCTANE
TETRACHLOROETHYLENE
CHLOR08ENZENE
ETHYLBENZENE
m,p - XYLENE
BROMOFORM
STYRENE
1 ,1 ,2,2 • TETRACHLOROETHANE
0 - XYLENE
1,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.S-BUTADIENE
RUVT 16280
7/23/99
8/10/99
L9HJ013
ppbv
1.45
0.67
0.80
0.62
ND
ND
0.08
ND
ND
ND
0.37
NO
ND
0.10
0.11
ND
ND
0.4D
0.91
ND
ND
ND
ND
ND
ND
0.07
0.65
0.11
ND
ND
ND
NO
ND
ND
ND
ND
ND
ND
1.68
ND
ND
0.1D
0.03 U
ND
0.26
0.66
ND
0.07 U
ND
0.34
0.11
0.29
ND
ND
ND
ND
0.06 U
0.04 0
RUVT 1627$
8/4/99
8/16/99
L9HP009
ppbv
1.24
0.76
0.71
0.64
ND
ND
0.07
ND
ND
1.05
0.43
ND
ND
0.10
0.10
NO
ND
0.21
0.74
ND
ND
ND
0.03 U
ND
ND
0.07
0.45
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.40
ND
ND
O.t1
0.03 U
ND
0.21
0.52
ND
0.07 U
ND
0.26
0.08
0.22
ND
ND
ND
ND
ND
ND
RUVT 16487
8/16/99
9/3/39
L9IB017
ppbv
1.21
0.61
0.68
0.58
ND
ND
0.07
ND
ND
ND
0.30
ND
ND
o.oa u
0.11
ND
ND
0.32
0.33
NO
ND
'NO
ND
ND
ND
0.06 U
0.60
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.38
NO
ND
0.15
0.06 U
ND
0.27
044
ND
0.07 U
ND
0.30
0.09
0.26
ND
ND
NO
ND
ND
ND
RUVT 1 6609
8/28/99
9/14/99
L9IN012
ppbv
1.35
0.87
0.68
0.66
ND
ND
0.06
ND
ND
ND
0.33
ND
ND
0.13
0.09
ND
ND
0.34
0.43
ND
ND
ND
ND
NO
ND
0.06 U
0.68
0.09 .
ND
NO
ND
ND
ND
ND
ND
NO
ND
NO
1.41
ND
ND
0.11
0.05 U
ND
0.24
0.61
ND
0.06 U
ND
0.31
0.09
0.24
ND
ND
0.03 U
ND
ND
ND
U = Under Detection Limit
ND - Not Detected
V n Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Rutland, VT (RUVT)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1,1 -DICHLOROETHANE
METHYL tsrt-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-DICHLOROETHYLENE
BROMOCHLQROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1 ,2 - DICHLOROETHANE
1,1,1 - TR1CHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - OICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1 ,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans • 1,3 - DICHLOROPROPENE
1,1.2-TRiqHLQROeTHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
itv.P-XYLENB
BROMOFORM
STYRENE
1 ,1 ,2,2 - TETRACHLOROETHANE
o - XYLENE
1,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIM ETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 • DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1 .3-8UTADIENE
RUVT 16807
9/9/99
10/6/33
L9JF010
ppbv
1.47
0,7?
0.71
0.83
ND
ND
0.09
ND
ND
NO
0.33
ND
ND
0.10
0.10
NO
ND
0,39
0.46
ND
ND
ND
ND
ND
ND
0,06
0.68
0.10
ND
ND
ND
ND
0.03 U
NO
ND
ND
ND
ND
1.65
NO
ND
0,14
0.07 U
ND
0.29
0.74
ND
0.09 U
ND
0,36
0.11
0.29
0.04 U
ND
0.04 U
ND
ND
ND
RUVT 16899
9/21/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
U = Under Detection Uirit
ND = Not Detected
V* Voided
Vt88_99
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Texarkana, AK (GREY)
Yearly Report (September 1998 - March 1999)
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYUENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
CIS-1.2-DICHLOROETHYLENE
8ROMOCHLOROMETHANE
CHLOROFORM
ETHYL f ert-BUTYL ETHER
1,2- DICHLOROETHANE
1,1,1 •TR1CHLOROE7HANE
BENZENE
CARBON TETRACHLORIDE
lert-AMYL METHYL ETHER
1,2 » DtCHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
0-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2.4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
o - DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
GREY 14556
9/1/98
PPbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
GREY 14695
9/6/98
PPbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
GREY 14886
9/17/99
PPbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
GREY 15096
10/8/98
10/22/98
U8JV014
ppbv
0.37
0.33
0.55
0.58
NO
NO
ND
NO
ND
ND
0.26
0,63
ND
0.20
0.08
JJO * -"•••
ND
ND
0.62
NO
ND
ND
ND
ND
ND
0.05 U
0.37
04)7 U
ND
ND
ND
NO
ND
ND
ND
ND
ND
ND
0.27
ND
ND
ND
ND
NO
0.08 U
0.14
ND
0.16
ND
0.08
0.07 U
0.24
ND
NO
ND
ND
ND
ND
U * Under Detection Lima
ND ° Not Detected
V»VoM
PARRGREY98JIB
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Texarkana, AK (GREY)
Yearly Report (September 1998 - March 1999)
SAMPLE SITES
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans-1,2-DICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL t«rt-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 - DICHLOROETHANE
1.1,1 -TR1CHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
U.OICHLOROPROPANE
ETHYL ACRYLATE
BROMOOICHLOROMETHANE
TRICHLOROETHYLENE
METHYL «ETHACRYLATE
cis -1,3 • DICHLOROPROPENE
METHYL1SOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 -TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
nvp>XYLENE
BROMOFORM
STYRENE
1,1,2,2 -TETRACHLOROETHANE
O.XYLENE
1 ,3,5-TRIMETHYLBENZENE
1,2,4-TRlMETHYLBENZENE
m-DICHLOROBENZENE
CHLOROMETHYLBENZENE
p • DICHLOROBENZENE
0-DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTAD1ENE
GREY 15118
10/14/98
10/30/98
L8J%010
ppbv
1.00
0.75
0.64
0.76
ND
ND
ND
0.17
ND
0.21 U
0.37
0.88
ND
0.25
0.07
ND
ND
ND
0.76
ND
ND
ND
ND
ND
ND
0.06
0.53
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.44
ND
ND
0.09 U
ND
ND
0.09 U
0,18
ND
0.11 U
ND
0.09
0.03 U
0.10
ND
ND
ND
ND
ND
ND
GREY 15441
10/25/98
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
GREY 16173
11/7/98
11/12/98
L8KK022
ppbv
1.81
O.S5
0.54
0.58
ND
ND
ND
0.03 U
ND
ND
0.26
1,01
ND
0.27
0.07
ND '
ND
ND
0.58
NO
ND
ND
ND
NO
ND
0.06 U
0.42
0.09
ND
ND
ND
NO
ND
ND
ND
ND
ND
ND
0.24
ND
ND
0.06 U
ND
NO
0.07 U
0.11
ND
0.10 U
ND
0.08 U
' 0.04 U
0,08 U
ND
ND
ND
ND
ND
ND
GREY 1521 9
11/15/98
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
U« Under Detection UmH
ND ° Not Detected
v-vow
PARROREYM.et
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) • Texarkana, AK (GREY)
Yearly Report (September 1998 - March 1999)
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1,1 - OICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BOTYL ETHER
1.2 • DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 • DICHLOROPROPANE
ETHYL ACRYLATE
BROMOmCHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 • DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans • 1,3 - DICHLOROPROPENE
1,1,2 -TRtCHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p*XYLENE
BROMOFORM
STYRENE
1.1,2,2 - TETRACHLOROETHANE
0-XYLENE
1.3.5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0. DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
GREY 15239
12/3/98
12/8/98
L8LH016
ppbv
2.00
0.30
0.57
0.65
ND
ND
ND
ND
ND
5.12
0.44
ND
ND
0.22
0.08
s ND
ND
ND
0.55
ND
ND
ND
ND
ND
ND
0.05 U
0.41
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.35
ND
ND
0.03 U
ND
ND
0.07 U
0.11
ND
0.08 U
ND
0.08
0.04 U
0.08 U
ND
ND
ND
ND
ND
ND
GREY 152S8
12/13/98
12/23/98
L8LV011
ppbv
1.26
0.72
0.66
0.73
ND
ND
ND
ND
0.55
ND
0.36
ND
ND
0.54
0.10
ND
ND
ND
1.84
ND
ND
ND
ND
ND
ND
0.10
0.48
0.11
ND
ND
ND
ND
ND
ND
ND
0.21
ND
ND
5.29
ND
ND
0.14
0.14
ND
0.34
o.ei
ND
0.35
ND
0.33
0.11
0.35
ND
ND
ND
ND
ND
ND
GREY 15286
12/26/96
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
GREY 16312
1/6/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
U« Under Detection Unit
NO-Not Detected
PARRGREY9B_S9
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Texarkana, AK (GREY)
Yearly Report (September 1998 - March 1999)
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHUOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOM ETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans <1,2 -OICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tert'BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL t«rt»BUTYL ETHER
1.2 - DICHLOROETHANE
1,1,1 -TRICflLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1.2.0ICHLOROPROPANE
ETHYL ACRYLATE
BROMOOICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans • 1,3 - DICHLOROPROPENE
1,1,2 - TRICHLOROETHANE
TOLUENE
OIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHUOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
0 - XYLENE
1 ,3,5-TRIMETHYLBENZENE
1A4+TRIMETHYL8ENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0* DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
GREY 15364
1/18/99
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
GREY 15370
1/30/99
PPbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
GREY 15419
2/11/99
2/23/99
L9EWOQ9
PPbv
0.49
0.98
0.61
0.84
ND
NO
ND
ND
ND
ND
0.29
ND
ND
0.13
0.09
ND
ND
ND
0.52
ND
ND
NO
ND
ND
ND
0.04 U
0.53
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.26
NO
ND
0.07 0
ND
ND
0.08 U
0.1J
ND
0.18
ND
0.08
0.06 U
- 0.09
ND
ND
ND
ND
ND
ND
GREY 16439
2/23/99
3/4/99
L9CD015
PPbv
0.60
0.30
0.50
0.56
ND
ND
ND
ND
ND
ND
0.33
ND
ND
0.13
0.07
ND
ND
ND
1.03
ND
ND
ND
ND
ND
ND
0.04 U
0.26
0.05 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.16
ND
ND
0.03 U
ND
ND
0.02 U
0,04 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
U * Under Detection Limit
ND°= Not Detected
VVoM
PARRGREY8S_«9
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) - Texarkana, AK (GREY)
Yearly Report (September 1998 - March 1999)
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYtENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1.2 - DICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tert-BOTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL lert-BUTYL ETHER
1.2 - DICHLOROETHANE
1.1,1 -TRICHLOROETOANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
J,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHUOROHETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBOTYL KETONE
trans - 1,3 • DICHLOROPROPENE
1,1,2 • TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1.2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1.1,2,2 - TETRACHLOROETHANE
0«XYLENE
1,3,5-TRIMETHYLBENZENE
1,2.4'TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0- DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADmNE
GREY 16487
3/7/99
3tt2/99
L9CL008
PPbv
0.81
0.29
0.62
0.66
ND
ND
ND
ND
ND
ND
0.28
ND
ND
0.11
0.09
ND
ND
ND
1.21
ND
ND
ND
ND
ND
ND
0.07
0.32
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.21
ND
ND
ND
ND
ND
0.06 U
0.10
ND
0.06 U
ND
0.06
0.03 U
0.06 U
ND
ND
ND
ND
ND
ND
GREY 15507
3/13/99
3/17/99
L9CQ010
PPbv
0.89
0.32
0.54
0.63
ND
ND
ND
ND
ND
ND
0.26
ND
ND
0.17
0.08
ND
ND
ND
0.56
ND
ND
ND
ND
ND
ND
0.04 U
0.31
0.07 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.27
ND
ND
0.04 U
ND
ND
0.06 U
0.09
ND
O.OS U
ND
0.05
0.03 U
0.06 U
ND
ND
ND
ND
ND
ND
GREY 15530
3rt9/fl9
3/24/99
L9CX011
PPbv
1.03
0.44
0.62
0.65
ND
ND
ND
ND
ND
6.19
0.28
ND
ND
0.39
0.09
ND
ND
ND
1.05
ND
ND
ND
ND
ND
ND
0.06
0.38
0.05 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.45
ND
ND
0.07 U
ND
ND
0.13
0,20
ND
0.25
ND
0.10
0.03 U
0.09
ND
ND
ND
ND
ND
ND
GREY 15564
3/25/89
4/16/99
L9DP005
ppbv
1.51
0.46
0.62
0.66
ND
ND
ND
ND
ND
8.96
0.32
ND
ND
0.28
0.08
NO
ND
ND
2.11
NO
ND
ND
ND
NO
ND
O.OS U
0.58
0.10
ND
ND
ND
ND
ND
ND
ND
0.09
ND
ND
5.53
ND
ND
0.09
ND
NO
0.30
0.41
ND
0.74
ND
0.22
0.06 U
0.13
ND
ND
ND
NO
ND
ND
U = Under Detection Unit
ND = Not Detected
PARROREV98.M
-------
1998/1999 UATMP (Urban Air Toxics Monitoring Program) • Texarkana, AK (GREY)
Yearly Report (September 1998 - March 1999)
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLON1TRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLQROPRENE
cls-1,2-OICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1.2 • DICHLOROETHANE
1,1.1 -TRICHLOROETMANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 * DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 • DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 • TRICHLOROETHANE
TOLUENE
DIBKOMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1,1,2,2 • TETRACHLOROETHANE
o-XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4.TRIMETHYLBEMZENE
m - DICHLOROBENZENE
CHLOROMETHYL8ENZENE
p - DICHLOROBENZENE
0. DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLOR0.1,3-BUTADIENE
GREY 16622
3/31/99
4/21/99
L9DU011
ppbv
0.71
0.3$
0.59
0.65
ND
NO
ND
ND
ND
8.86
0.30
ND
ND
0.37
0.09
ND
ND
ND
3.28
ND
ND
NO
ND
ND
ND
0.07
0.46
0.05 U
ND
NO
ND
ND
0.10
NO
ND
NO
ND
ND
0.47
ND
ND
0.08 U
ND
ND
0.49
0.61
ND
1.S5
ND
0.34
0.06 U
0.10
ND
NO
ND
ND
ND
ND
U = Under Detection LMI
NO = Not Detected
VVoB
PARRGR£Y«8_M
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Underbill, VT (UNVT)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYUENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1.2-DICHLOROETHYLENE
8ROMOCHLOROMETHANE
CHLOROFORM
ETHYL tBrt-BUTYL ETHER
1,2 -DICHLOROETHANE
1.1,1 - TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBOTYL KETONE
trans • 1 ,3 • DICHLOROPROPENE
1 ,1 ,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p - XYLENE
BROMOFORM
STYRENE
1,1,2,2 - TETRACHLOROETHANE
o - XYLENE
1,3,5-TRIMETHYLBENZENE
1 JI,4-TRIMETH YLBEN2ENE
m - DICHLOROBENZENE
CHLORQMETHYLBENZENE
p - DICHLOROBENZENE
0- DICHLOROBENZENE
1.2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
UNVT 14680
SO/98
9/25/98
L8IY015
ppbv
1.07
0.24
0.75
0.49
ND
NO
ND
ND
ND
ND
0.39
ND
ND
ND
0.39
•~ ND
ND
ND
0.53
ND
ND
ND
ND
ND
ND
O.OE
0.17
0.12
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.19
ND
ND
ND
ND
ND
0.08 U
0.41
ND
ND
ND
O.OB
0.03 U
0.07 U
ND
ND
ND
ND
ND
ND
UNVT14816
9/14/98
10/19/98
L8JS021
ppbv
0.42
0.32
0.62
0.68
ND
ND
ND
ND
ND
ND
0.58
ND
ND
1.29
0.08
ND - - -
ND
ND
0.38
ND
ND
ND
ND
ND
ND
0.03 U
0.22
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.26
ND
ND
ND
ND
ND
0.06 U
0,09
ND
0.03 U
ND
0.06
0.03 U
0.06 U
ND
ND
ND
ND
ND
ND
UNVT 15052
9/26/98
10/22/98
L8JV008
ppbv
0.46
0.19
0.56
0.49
ND
ND
ND
ND
ND
ND
0.27
ND
ND
0.09 U
0.08
- ND
ND
ND
0.35
ND
ND
NO
ND
ND
ND
0.04 U
0.25
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
NO
0.28
NO
ND
ND
ND
ND
0.07 U
0.10
ND
.0.04 U
ND
O.OB
0.44
0.71
ND
NO
ND
ND
ND
ND
UNVT 161 09
10/8/98
10/22/98
L8JV01S
ppbv
0.58
0.29
0.60
0.56
ND
ND
ND
ND
ND
0.34
0.52
ND
ND
0.20
0.06
ND
ND
ND
0.43
ND
ND
ND
ND
ND
ND
0.06
0.31
0.07 U
ND
ND
ND
ND
NO
ND
ND
ND
ND
NO
0.56
NO
ND
ND
ND
ND
0.13
0,15
ND
ND
ND
0.09
0.03 U
0.07 \i
ND
ND
ND
ND
ND
NO
U = Under Detection Umll
ND = Not Detected
V = Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Underbill, VT (UNVT)
Yearly Report (September 1998 - September 1999 )
SAMPLE site #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
8ROMOMETHANE
CHLOROETHANE
ACETONITWLE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICMLOROETHYLENE
1,1 -DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1 ,2-DICHLOROETHYLENE
BROMOCHLDROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 • DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1 2- D1CHLOROPROPANE
ETHYL ACRYLATE
8ROMODICHLOROM ETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1.3 • DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1.1.2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROM ETHANE
1.2-DIBROMOETHANE
N-QCTANg
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m.p - XYLENE
BROMOFORM
STYRENE
1.1 ,2,2 - TETRACHLOROETHANE
0 - XYLENE
1 ,3,5-TRIMETHYLBENZENE
1A4-TRIMETHYLBENZEN£
m - DICHLOROBENZENE
CHLOROM ETHYLBENZENE
p- DICHLOROBENZENE
0- DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
UNVT 15139
10/20/98
10/30/98
L8J%OOS
ppbv
0.32
0,16
0.39
0.42
ND
ND
ND
ND
ND
ND
0.05
ND
ND
ND
0.05
ND
ND
ND
0.26
ND
ND
ND
ND
ND
ND
ND
0.13
0.06 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.10
ND
ND
ND
ND
ND
0.02 U
0.02 U
ND
ND
ND
ND
0.02 U
0.06 U
ND
ND
ND
ND
ND
ND
UNVT161B9
11/1/88
11/18/98
L8KR007
ppbv
0.51
0.21
0.57
0.59
ND
ND
ND
ND
ND
ND
0.28
ND
ND
0,03 U
0.09
ND
ND
ND
0.26
ND
ND
ND
ND
ND
ND
0.04 U
0.25
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.18
ND
ND
NO
ND
ND
0.06 U
0.09
ND
ND
ND
0.03
ND
0.05 U
ND
ND
ND
ND
ND
ND
UNVT 16199
11/13/98
12/1/98
L8LA011
ppbv
0.74
0.2B
0.60
0.62
ND
ND
ND
ND
ND
ND
0.30
ND
ND
ND
0.08
ND
ND
ND
0.34
ND
ND
ND
ND
ND
ND
0.05 U
0.25
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.35
ND
ND
ND
ND
ND
0.07 U
0.10
ND
0.06 U
ND
0.06
0.05 U
0.10
ND
NO
ND
ND
ND
ND
UNVT 16226
11/26/88
12/8/98
L8LH010
ppbv
0.52
0.13
0.56
0.61
ND
ND
ND
ND
ND
WO
0.25
ND
ND
ND
0.08
ND
ND
ND
0.11
ND
ND
NO
ND
NO
ND
0.05 U
0.23
0.11
ND
ND
ND
ND
ND
NO
ND
NO
ND
ND
0.16
ND
ND
ND
ND
ND
0.05 U
0.07 U
ND
ND
ND
0.03
ND
O.OS U
ND
ND
ND
ND
ND
ND
U « Under Detection Limit
ND= Not Delected
V = Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Underbill, VT (UNVT)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITES
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2-DICHLOROETHYLENE
1,1 -DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1 ,2-DICHLOROETHYLENE
BROMOCHLORDMETHANE
CHLOROFORM
ETHYL tett-BUTYL ETHER
1,2 -DICHLOROETHANE
1.1,1 • TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - DJCHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1 ,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1 ,1 ,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p • XYLENE
BROMOFORM
STYRENE
1 ,1 ,2,2 -TETRACHLOROETHANE
o - XYLENE
1,3,5-TRIMETHYLBENZENE
1,2,4-TRIMETHYLBENZENE
m -DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 • DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
UNVT 16247
12/7/98
12/31/98
L8LV009
ppbv
0.59
0.22
0.64
0.71
ND
ND
ND
ND
ND
ND
0.31
ND
ND
ND
0.10
ND
ND
ND
0.26
ND
ND
ND
ND
ND
ND
0.07
0.28
0.11
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.20
NO
ND
ND
ND
ND
0.06 U
0.09
ND
ND
ND
0.06
0.03 U
0.06 U
ND
ND
ND
ND
ND
ND
UNVT 16288
12/19/98
1/11/99
L9AK010
ppbv
1.57
0.47
0.65
0.65
ND
ND
ND
ND
ND
5.85
0.40
ND
ND
0.19
0.09
ND
ND
ND
0.44
ND
ND
ND
ND
ND
ND
0.06
0.35
0.07 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.32
ND
ND
0.08 U
ND
ND
0.16
0.26
ND
0.09 U
ND
0.14
0.05 U
0.09
ND
ND
ND
ND
ND
ND
UNVT 15308
12/31/98
1/21/99
L9AU007
ppbv
0.92
0.22
0.62
0.63
ND
ND
ND
ND
ND
ND
0.29
ND
ND
0.40
0.09
ND
ND
ND
0.27
ND
ND
ND
ND
ND
ND
0,05 U
0.06
0X19
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.1B
ND
ND
ND
ND
ND
0.05 U
0.06 U
ND
0.03 U
ND
~0.04
0.03 U
0.05 0
ND
ND
ND
ND
ND
ND
UNVT 16322
1/12/99
1/21/99
L9LAU011
ppbv
1.03
0.32
0.62
0.71
ND
ND
ND
ND
ND
ND
0.31
ND
ND
0.35
0.09
ND
ND
NO
0.16
ND
ND
ND
ND
ND
ND
0.07
0.40
0.09
ND
ND
ND
ND
ND
NO
ND
ND
ND
ND
0.31
ND
ND
ND
ND
ND
0.06 U
0.11
ND
0X13 U
ND
0.07
0.03 U
0.06 U
ND
ND
ND
ND
ND
ND
U = Under Detection Umil
NO = Not Delected
V * Voided
\rt9B_99
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Underbill, VT (UNVT)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROM ETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITmLE
1,1-DICHLOROETHENE
METHYLENECHLORiDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1,1 -DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1 ,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 - DICHLOROETHANE
l.f.1 - TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,Z- D1CHLDROPROPANE
ETHYL ACRYLATE
BROMODICHUOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
CIS -1 ,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1 ,3 - DICHLOROPROPENE
1,1.2 - TRICHLOROETHANE
TOLUENE
OIBROMOCHLOROM ETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBEN2ENE
ETHYLBENZENE
W-P-XYLENE
BROMOFORM
STYRENE
1 ,1 ,2,2 - TETRACHLOROETHANE
o-XYLENE
1,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIMETHYLBEN2ENE
m - DICHLOROBENZENE
CHLOROMeTHYLBENZENE
p • DICHLOROBENZENE
0- DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
UNVT 15358 01
1/24/99
2/3/99
L9BB01S
ppbv
0.66
0.23
0.62
0.70
NO
NP
ND
ND
ND
2.47
0.30
ND
ND
0.03 U
0.11
ND
ND
ND
0.24
ND
ND
ND
ND
ND
ND
0.05 V
0.26
0.09
ND
NO
ND
ND
ND
NO
ND
ND
ND
ND
0.27
ND
ND
NO
ND
ND
0.07 U
0.11
ND
0.04 U
ND
0.07
0.04 U
0X17 U
ND
NO
ND
ND
ND
ND
UNVT16368R1
1/24799
2/9/93
L9BI011
ppbv
0.63
0.23
0.63
0.70
ND
ND
ND
ND
ND
2.S3
0.29
ND
ND
ND
0.10
ND
ND
NO
0.33
ND
ND
ND
ND
ND
ND
0.04 U
0.27
0.07 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
NO
0.27
ND
ND
0.05 U
ND
ND
0.08 U
0,12
ND
0,04 U
ND
0.08
0.05 U
0.09
ND
NO
ND
ND
ND
NO
UNVT1$36002
1/24/99
2/3/99
L9BB016
ppbv
0.69
040
0.60
0.68
ND
ND
ND
ND
ND
0.37
0.29
ND
ND
NO
0.08
ND
ND
ND
0.15
ND
ND
NO
ND
ND
ND
0.05 U
0.28
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
'ND
0.24
ND
ND
ND
ND
ND
0.07 U
0.11
ND
0.04 U
ND
0.07
0.03 U
0.07 U
ND
NP
ND
NO
ND
ND
UNVT 16360 R2
1/24/99
2/11/99
L9BJ006
ppbv
V
V
V
V
V
v •
V
V
V
V
V
V
V
V
V
V '-••"••'
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
U = Under Detection Limit
ND = Not Detected
V = Voided
V198_S9
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Underbill, VT (UNVT)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1.1-DICHLOROETHENE
METHYLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans • 1,2 - DICHLQROETHYLENE
1,1-DICHLOROETHANE
METHYL tert-BUTYL ETHER
M ETHYL ETHYL KETONE
CHLOROPREN6
cls-1,2-DICHLOROETHYLENE
SROMOCHLOROM ETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1 ,2 - DICHLOROETHANE
1.1,1 • TRICHLORQETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1.Z- OICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1 ,3 - DICHLOROPROPENE
METHYL ISOBOTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1 ,1,2 - TRICHLORQETHANE
TOLUENE
OIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p - XYLENE
BROMOFORM
STYRENE
1 ,1 ,2,2 - TETRACHLOROETHANE
o - XYLENE
1 ,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0- DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
UNVT1641T
2/5/99
3/4/99
L9CD006
ppbv
0.57
0.17
0.54
0.62
ND
ND
0.09
ND
ND
2.6B
0.27
ND
ND
0.03 U
0.08
ND " ~
ND
ND
0.57
ND
ND
ND
ND
ND
ND
0.06
0.20
0.05 U
ND
ND
0.16
ND
ND
0.07
ND
0X3
ND
ND
0.16
ND
ND
ND
ND
ND
0.05 U
0.07 U
ND
0.10 U
0.04 U
0.03 U
0.06 U
0.12
0.08 U
ND
0.09
0.11
0.41
0.27
UNVT1S447
2/17/99
3/4/99
L9C0011
ppbv
0.80
0.1 S
0.51
0.61
ND
ND
ND
ND
ND
ND
0.21
ND
ND
0.06 U
0.08
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.05 U
0.25
0.07 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.21
ND
ND
NO
ND
ND
0.03 U
0.05 U
ND
ND
ND
0.03 U
ND
ND
ND
ND
ND
ND
ND
ND
UNYM6486
3/1/99
3/11/99
L9CJ020
ppbv
1.15
0.34
0.63
0.71
ND
ND
ND
ND
ND
1,15
0.36
ND
ND
ND
0.10
ND
ND
ND
0.56
ND
ND
ND
ND
ND
ND
'0.16
0.36
0.07 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.46
ND
ND
0.05 U
ND
ND
0.09 U
0.13
ND
0.05 U
ND
0.09
0.03 U
0.07 U
ND
ND
ND
ND
ND
ND
UNVT 15644
3/13/99
3/24/99
L9CX012
ppbv
0.80
0.24
0.62
0.72
ND
ND
ND
ND
ND
ND
0.29
ND
ND
ND
0.10
ND ' •"•
ND
ND
0.42
ND
ND
ND
ND
ND
ND
0.03 U
0.31
0.08 0
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.18
ND
ND
0.02 U
ND
ND
0.05 U
0,05 U
ND
0.02 U
ND
0.04 U
0.01 U
0.04 U
ND
ND
ND
ND
ND
NO
U = Under Defection Until
NO = Not Detected
V = Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Underbill, VT (UNVT)
Yearly Report (September 1998 - September 1999 )
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETMANE
CHLOROETHANE
ACETONITR&E
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-OICHLOROETHENE
METHYLS^ CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans • 1,2 • DICHLOROETHYLENE •
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
CIS-1.2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 - DICHLOROETHANE
1,1,1 - TRIOHUOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1 A- DICHLOROPRDPANE
ETHYL ACRYLATE
BROMOOICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBOTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1 ,1 ,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTAKE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
nt,p - XYLENE
BROMOFORM
STYRENE
1 ,1 ,2,2 - TETRACHLOROETHANE
o - XYLENE
1,3,5-TRIMETHYLBENZENE
1 ,2,4-TftlMETH YLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYUBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
UNVT 16S68
3/19/99
4/12/99
L9DL012
ppbv
0.71
04!5
0.66
0.74
ND
ND
ND
ND
ND
ND
0.09
ND
ND
ND
0.09
ND
ND
ND
0.41
ND
ND
ND
ND
ND
ND
0,06
0.26
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.14
ND
ND
ND
ND
ND
0.05 U
O.QS U
ND
0.03 U
ND
0,05
0.03 U
0.06 U
ND
ND
ND
ND
ND
ND
UNVT 16580 D1
3/26/99
4/22/99
L9DU014
ppbv
0.61
0.22
0.60
0.68
ND
ND
ND
ND
ND
ND
0.34
ND
ND
0.10 U
0.09
ND
ND
ND
0.88
ND
ND
ND
ND
ND
ND
0.04 U
0.20
0.04 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.15
0.00
ND
0.05 V
ND
ND
0.06 U
0,08
ND
0.04 U
ND
0.05
0.03 U
0.06 U
ND
ND
ND
ND
ND
ND
UNVT 15580 R1
9125199
4/23/99
L9DV01S
ppbv
0.60
0,22
0.61
0.69
ND
NP
ND
ND
ND
ND
0.36
ND
ND
0.16
0.09
ND
ND
ND
0.85
ND
ND
ND
ND
ND
ND
0.05 U
0.20
0.04 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.15
ND
0.00
0.05 U
ND
ND
0.05 U
0.07 U
ND
0.03 U
ND
0.04
0.02 U
0.03 U
ND
ND
ND
ND
ND
ND
UNVT 16582 02
3/26/99
4/22/99
L9DU016
ppbv
0.62
0.21
0.61
0,68
ND
ND
ND
ND
ND
ND
0.35
ND
ND
0.18
0.09
* ~ NO
ND
ND
0.46
ND
ND
ND
ND
ND
ND
0.04 U
0.22
0.07 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.13
ND
ND
ND
ND
ND
0.04 U
0.07 U
ND
0.03 U
ND
0.05
0.03 U
0.05 U
ND
ND
ND
ND
ND
ND
U = Under Detection Limit
ND * Not Detected
V = Voided
Vtes.89
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Underbill, VT (UNVT)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-OICHLOROETHENE
METH YLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1,2 - DICHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1 ,2-DICHLOROETH YLENE
BROMOCHLDRDMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2-DICHLOROETHANE
1,1.1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1 ,2 - D1CHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1 ,3 - DICHLOROPROPENE
1 ,1 .2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p • XYLENE
BROMOFORM
STYRENE
1 .1 ,2,2 - TETRACHLOROETHANE
o • XYLENE
1,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIMETHYLBEN2ENE
m . DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTAD1ENE
UNVT 15582 RZ
3/25/99
5/7/99
L9ED032
ppbv
0.62
0.25
0.63
0.64
NO
ND
ND
ND
ND
ND
0.44
ND
ND
0.33
0.10
ND
ND
ND
0.67
ND
ND
NO
ND
ND
ND
O.OT
0.22
0.07 U
ND
ND
ND
ND
ND
NO
ND
NO
ND
ND
0.14
ND
ND
O.O4 U
ND
ND
O.OS U
0.07 U
ND
0.03 U
ND
0.05
0.03 U
0.05 U
ND
ND
ND
ND
ND
ND
UNVT 15642
4/6/89
4/22/99
L9DV006
ppbv
0.98
0.24
0.59
0.74
ND
ND
ND
ND
ND
ND
0.30
ND
ND
O.OB U
0.09
ND
ND
NO
0.39
ND
ND
ND
ND
ND
ND
O.OS U
0.28
0.08 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.22
ND
ND
ND
ND
ND
0.07 U
0.11
ND
ND
ND
0.07
0.04 U
O.OS U
ND
ND
ND
NO
ND
ND
UNVT 16666
4/12/99
6/10/99
L9EJ012
ppbv
0.61
0.24
0.64
0.71
ND
ND
ND
ND
ND
ND
0.37
ND
ND
0.06 U
0.10
ND
ND
ND
0.37
ND
ND
ND
ND
ND
ND
0.06
0.25
0X18 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.19
ND
ND
0.05 U
ND
ND
0.06 U
0.09
ND
0.03 U
ND
0.07
0.04 U
-0.05 U
ND
ND
ND
ND
ND
ND
UNVT 16735
4/30/99
5/18/99
L9ER010
ppbv
0.53
0.29
0.68
0.76
ND
ND
ND
ND
ND
ND
0.31
ND
ND
0,22
0.10
NO ' "
ND
ND
0.63
KID
ND
ND
ND
ND
ND
0.07
0.17
0.09
ND
ND
ND
ND
ND
NO
ND
ND
ND
NO
0.19
ND
ND
0.04 U
ND
ND
0.06 U
0.08 U
ND
0X13 U
ND
O.OS
0.03 U
0.05 U
ND
ND
ND
ND
ND
ND
U = Under Detection Umll
NO - Not Detected
V » Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Underbill, VT (UNVT)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLSNE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1.3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
AQETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METH YtENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans • 1,2 • DICHLOROETHYLENE
1,1 - DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1 ,2-DICHLOROETH YLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2 - DICHLOROETHANE
1.1.1 .TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2- DICHLOROPROPANE
ETHYL ACRYLATE
BROMOOICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL ISOBOTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2 • TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
NtOCtANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p - XYtENE,
BROMOFORM
STYRENE
1 ,1 ,2,2 - TETRACHLOROETHANE
o - XYLENE
1,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIMETHYtBENZENE
tn • DICHLOROBENZENE
CHLOROM ETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO*1,3-BUTADIENE
UNVT 16799 01
6/12/99
6/7/99
L9FGOOT
ppbv
0.56
079
0.57
0.73
0.01 U
ND
ND
0.02 U
ND
ND
0.30
ND
ND
0.07 U
0.09
ND
ND
ND
0.48
ND
ND
ND
ND
ND
ND
0.09
0.16
0.06 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
NO
0.16
ND
ND
0,06 U
ND
ND
0.08 U
0.08 U
ND
O.OS U
ND
0,06
0.04 U
0.06 U
ND
ND
ND
ND
ND
ND
UNVT 1*799 K1
6/12/99
6/9/99
L9FI007
ppbv
0.54
0.29
0.56
0.72
0.01 U
ND
ND
0.02 U
ND
ND
0.62
ND
ND
0.09 U
0.10
ND
ND
ND
0.53
ND
ND
ND
ND
ND
ND
0.06
0.16
O.OS U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.19
ND
ND
0.06 U
ND
ND
0.09 U
0,10
ND
0.06 U
ND
0.07
0.06 U
0.08 U
ND
ND
ND
ND
ND
ND
UNVT 16801 D2
5/12/99
6/7/99
L9FG008
ppbv
0.45
0,29
0.54
0.67
0.02 U
ND
ND
ND
ND
ND
0.26
ND
ND
0.13
.0.10
ND
ND
ND
0.38
ND
ND
ND
ND
NO
ND
0,07
0.14
0.01 U
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.16
,ND
ND
0.06 U
ND
ND
0.06 U
0.07 U
ND
0.04 U
ND
0.05
0.04 U
0.06 U
ND
ND
ND
ND
ND
ND
UNVT 16801 R2
6/12/99
6/9/99
L9FIOOB
ppbv
0.52
0.27
0.54
0.66
0.01 U
ND
ND
0.01 U
ND
NO
0.30
ND
ND
0.11
0.09
ND
ND
ND
0.39
ND
ND
ND
ND
ND
ND
0.06
0.16
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
w
0.18
ND
ND
0.06 U
ND
ND
0.07 U
0.10
ND
0.06 U
ND
0.07
O.OS U
0.08 U
ND
ND
ND
ND
ND
ND
U = Under Detection Unit
ND = Not Detected
V = Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Underbill, VT (UNVT)
Yearly Report ( September 1998 - September 1999 )
SAMPtC SITES
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENE
DICHLORODIFLUOROMETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITR1LE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METH YLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans- 1,2 -DICHLOROETHYLENE -
1.1 -DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cis-1,2-DICHLOROETHYLENE
8ROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1 ,2 - DICHLOROETHANE
1,1,1 - TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2 - DJCHLDRDPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1.3 - DICHLOROPROPENE
METHYt ISOBUTYL KETONE
trans - 1 ,3 - DICHLOROPROPENE
1 ,1 ,2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBEN2ENE
ETHYLBENZENE
m,p - XYLENE
BROMOFORM
STYRENE
1, 1,2,2 -TETRACHLOROETHANE
o - XYLENE
1 ,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLQROMETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1.3-BUTADIENE
UNVT 18791
5/24/99
6/7/99
L9FG009
ppbv
0.48
0.26
0.55
0.76
0.01 U
NO
ND
0.02 U
ND
ND
0.28
0.30
ND
0.06 U
0.09
ND
ND
ND
0.32
ND
ND
ND
0.01 U
ND
ND
0.07
0.15
o.to
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.15
ND
ND
0.06 U
0.01 U
ND
0.06 U
0.08 U
ND
0.03 U
ND
0.05
0.04 U
0.06 U
ND
ND
ND
ND
ND
ND
UNVT 16830
6/6/89
6/17/99
L9FQ010
ppbv
0.36
0.22
0.53
0.70
0.01 U
ND
ND
0.02 U
ND
ND
0.28
ND
ND
0.05 U
0.09
ND
ND
ND
0.36
ND
ND
ND
ND
ND
ND
0.07
0.13
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.16
ND
ND
0.06 U
0.01 U
ND
0.06 U
0.08
ND
0.03 U
ND
o.oe
0.04 U
0.06 U
ND
ND
ND
ND
ND
ND
UNVT 16923
6/17/99
6/29/99
L9FW07
ppbv
0.31
022
0.56
0.66
0.01 U
ND
ND
ND
ND
ND
0.53
ND
ND
0.09 U
0.09
ND
ND
ND
0.25
ND
ND
ND
ND
NO
ND
0.07
0.13
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
2.40
ND
ND
0,06 U
ND
NO
0.07 U
0.12
ND
0.04 U
ND
0.07
0.03 U
0.06 U
ND
ND
ND
ND
ND
ND
UNVT 16026
6/29/99
7/20/99
L90T008
ppbv
0.41
0.24
0.63
0.82
ND
ND
ND
ND
ND
ND
0.31
0.27
ND
0.06 U
0.09
• HO—-" *
ND
ND
0.47
ND
ND
ND
ND
ND
ND
0.06
0.17
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
1.11
ND
ND
0.16
ND
ND
0.24
0,83
ND
0.11
ND
0.43
0.11
0.31
ND
ND
0.02 U
ND
ND
ND
U = Under Detection Umll
NO - Not Detected
V • Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Underbill, VT (UNVT)
Yearly Report (September 1998 - September 1999 )
SAMPLE SITE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
ACETYLENE
PROPYLENB
DICHLORODIFLUOROM ETHANE
CHLOROMETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRJte
TRICHLOROFLUOROMETHANE
ACRYLONITRtLE
1.1-OICHLOROETHENE
METHYLENECHLPRIDE
TRICHLOROTRIFLUOROETHANE
trans* 1,2 - DICHLOROETHYLENE
1,1-DICHLOROETHANE
METHYL tert-BUTYL ETHER
METHYL ETHYL KETONE
CHLORQPRENE
cis-1 ,2-DICHLOROETH YLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-BUTYL ETHER
1,2-OICHLOROETHANE
1.1,1 -TRICHLQRflETHANe
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1,2- D1CHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
cis -1 ,3 • OICHLOROPROPENE
METHYL ISOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1 .1 .2 - TRICHLOROETHANE
TOLUENE
DIBROMOCHLOROM ETHANE
1 ,2-DIBROMOETHANE
N -OCTANE
TETRACHLOROETHYLENE
CHtOROBENZENE
ETHYLBENZENE
m,p - XYLENE
BROMOFORM
STYRENE
1 ,1 ,2,2 - TETRACHLOROETHANE
o - XYLENe
1 ,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLOROMETHYLBENZENE
p - DICHLOROBENZENE
0 • DICHLOROBENZENE
1 ,2,4-TRICHLOROBENZENE
HEXACHLORO-1,3-BUTADIENE
UNVT 16265
7/17/99
8/10/99
L9HJ010
ppbv
0.22
0.14
0.67
0.98
ND
ND
ND
ND
ND
NP
0.52
ND
ND
0.09 U
0.11
ND
ND
NO
0.67
ND
ND
ND
ND
ND
ND
Ot07
0.17
0.12
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.20
ND
ND
0.05 U
ND
ND
0.06 U
o.oa
ND
0.03 U
ND
0,05
0.04 U
0.06 U
ND
ND
ND
ND
ND
ND
UNVT162S6
7/23/98
8/10/99
L9HJ011
ppbv
0.51
0.79
0.72
0.97
ND
ND
ND
ND
ND
ND
0.34
ND
ND
0.03 U
0.10
ND
ND
ND
0.58
ND
ND
ND
ND
ND
ND
0.07
0.16
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.21
ND
ND
D.OS U
ND
ND
0.06 U
0.09
ND
0.04 U
ND
0.05
0.04 U
0.05 U
ND
ND
ND
ND
ND
ND
UNVT 16273
8/4/99
8/16/99
L9HP008
ppbv
0.35
0.21
0.66
0.76
0.01 U
ND
ND
ND
ND
ND
0.40
0.25
ND
0.05 U
0.11
NO
ND
ND
0.39
ND
ND
ND
ND
ND
ND
0.06
0.11
0.10
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.14
ND
ND
0.03 U
ND
ND
0.06 U
O.Q7 U
ND
0.03 U
ND
0.05
0.04 U
0.06 U
ND
ND
ND
ND
ND
ND
UNVT 16491
8/16/99
9/3/99
UNBOiS
ppbv
0.23
0.31
0.53
0.61
ND
ND
ND
ND
ND
ND
0.26
ND
ND
0.05 U
0.09
ND
ND
ND
0.47
ND
ND
NO
ND
NO
ND
0.05 U
0.13
0.08 U
ND
NO
ND
ND
ND
ND
ND
0.09
ND
ND
0.18
ND
ND
0.04 U
ND
ND
0.05 U
0,11
ND
0.03 U
ND
0.05
0.03 U
' O.OS U
ND
ND
ND
ND
ND
ND
U = Under Detection limit
ND - Not Detected
V = Voided
-------
1998/99 UATMP (Urban Air Toxics Monitoring Program) - Underbill, VT (UNVT)
Yearly Report ( September 1998 - September 1999 )
SAMPLE SITE*
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
ACETYLENE
PROPVLENE
DICHLORODIFLUOROMETHANE
CHLOROM ETHANE
DICHLOROTETRAFLUOROETHANE
VINYL CHLORIDE
1,3-BUTADIENE
BROMOMETHANE
CHLOROETHANE
ACETONITRILE
TRICHLOROFLUOROMETHANE
ACRYLONITRILE
1,1-DICHLOROETHENE
METfl YLENE CHLORIDE
TRICHLOROTRIFLUOROETHANE
trans - 1 ,2 - DICHLOROETH YLENE
1,1 -DICHLOROETHANE
METHYL tert-SUTYL ETHER
METHYL ETHYL KETONE
CHLOROPRENE
cls-1 ,2-DICHLOROETHYLENE
BROMOCHLOROMETHANE
CHLOROFORM
ETHYL tert-SUTYL ETHER
1 ,2 - DICHLOROETHANE
1,1,1 -TRICHLOROETHANE
BENZENE
CARBON TETRACHLORIDE
tert-AMYL METHYL ETHER
1 ,2 - DICHLOROPROPANE
ETHYL ACRYLATE
BROMODICHLOROMETHANE
TRICHLOROETHYLENE
METHYL METHACRYLATE
els -1,3 - DICHLOROPROPENE
METHYL JSOBUTYL KETONE
trans - 1,3 - DICHLOROPROPENE
1,1,2- TRICHLOROETHANE
TOLUENE
D1BROMOCHLOROMETHANE
1,2-DIBROMOETHANE
N-OCTANE
TETRACHLOROETHYLENE
CHLOROBENZENE
ETHYLBENZENE
m,p-XYLENE
BROMOFORM
STYRENE
1 ,1 ,2,2 - TETRACHLOROETHANE
o • X YLENE
1,3,5-TRIMETHYLBENZENE
1 ,2,4-TRIMETHYLBENZENE
m - DICHLOROBENZENE
CHLORDMETHYLBENZENE
p - DICHLOROBENZENE
0 - DICHLOROBENZENE
1,2,4-TRICHLOROBENZENE
HEXACHLORO-1 ,3-BUTADIENE
UNVT 16620
8/28/93
ppbv
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
V
UNVT16801
9/9/99
10/6/99
L9JF011
ppbv
0.48
0.43
0.63
0.69
ND
NO
ND
ND
ND
ND
0.35
ND
ND
0.09 U
0.10
ND
ND
ND
1.06
ND
ND
ND
ND
ND
ND
0.05 U
0.19
0.09
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.57
ND
ND
0.09 U
ND
ND
0.12
0,18
ND
0.11 U
ND
0.10
0.06 U
0.11
ND
ND
ND
ND
ND
ND
UNVT 16890
9/21/99
10/11/99
L9JK009
ppbv
0.30
0.51
0.67
0.61
ND
ND
ND
ND
ND
ND
0.32
ND
ND
0.05 U
0.10
ND
ND
ND
0.90
ND
ND
ND
ND
ND
ND
0.06 U
0.16
0.11
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.25
ND
ND
0.05 U
ND
ND
0.07 U
0.14
ND
0.04 U
ND
0.07
0.04 U
0.06 U
ND
ND
ND
ND
ND
ND
U = Under Detection Umlt
ND = Nol Detected
V = Voided
-------
SNMOC OPTION REPORT
SITE CODE: BRVT
Brattleboro, VT
Reported in ppbv
Sample No.: 14684 14811 15054 15113
Sampling Date: 9/2/98 9/14/98 9/26/98 10/8/98
Analysis Date: VOID 10/19/98 10/22/98 10/22/98
Compound
Ethylene 1.42 1.60 1.89
Acetylene 1.02 1.16 1.18
Ethane 2.03 2.70 1.67
Propylene 0.56 0.57 0.66
Propane 8.25 4.51 3.20.
Propyne 0.02 0.02 0.03
Isobutane 1.24 1.14 0.79
lsobutene/1-Butene 0.20 0.20 0.23
1,3-Butadiene 0.06 0.06 0.10
n-Butane 1.49 1.91 1.46
trans-2-Butene 0.17 0.21 0.17
cis-2-Butene 0.19 0.21 0.19
3-Methyl-1-butene 0.04 0.06 0.04
Isopentane 5.82 4.22 3.13
1-Pentene 0.12 0.15 0.13
2-Methyl-1-butene 0.12 0.17 0.16
n-Pentane 1.04 1.02 0.74
Isoprene 0.35 0.23 . 0.15
trans-2-Pentene 0.18 0.22 0.19
cis-2-Pentene 0.13 0.15 0.13
2-Methyl-2-butene 0.19 0.24 0.19
2,2-Dimethylbutane 0.22 0.23 0.17
Cyclopentene 0.08 0.07 0.04
4-Methyl-1-pentene ND 0.01 ND
Cyclopentane 0.15 0.13 0.11
2,3-Dimethylbutane 0.48 0.61 0.44
2-Methylpentane 0.54 0.55 0.43
3-Methylpentane 0.37 0.35 0.28
2-MethyM-pentene 0.02 0.04 0.03
1-Hexene 0.02 0.02 0.03
2-Ethyl-1-butene ND ND ND
n-Hexane 0.62 0.32 0.27
trans-2-Hexene 0.01 0.03 0.03
cis-2-Hexene ND 0.02 0.01
Methylcyclopentane 0.23 0.20 0.18
2,4-Dimethylpentane 0.10 0.12 0.09
Benzene 0.41 0.45 0.47
Cyclohexane 17.18 0.19 0.29
2-Methylhexane 0.22 0.17 0.17
2,3-Dimethylpentane 0.16 0.16 0.15
3-Methylhexane 0.31 0.18 0.17
1-Heptene NO ND ND
2,2,4-Trimethylpentane 0.26 0.23 0.21
n-Heptane 0.29 0.13 0.15
Methylcyclohexane 0.16 0.10 0.12
2,2,3-Trimethylpentane 0.05 0.04 0.04
2.3,4-Trimethylpentane 0.09 0.09 0.09
Toluene 1.64 0.90 0.94
2-Methylheptane 0.06 0.06 0.06
3-Methylheptane 0.06 0.07 0.06
1-Octene 0.01 0.005 ND
n-Octane 0.10 0.07 0.08
Ethylbenzene 0.19 0.37 0.39
m-Xylene/p-Xylene 0.68 0.70 0.76
Styrene 0.18 0.13 0.14
o-Xylene 0.20 0.27 0.26
1-Nonene ND ND ND
n-Nonane 0.09 0.08 0.07
Isopropylbenzene 0.05 0.05 0.04
a-Pinene 0.24 0.12 0.14
n-Propylbenzene 0.07 0.06 0.05
m-Ethyltoluene 0.15 0.19 0.17
p-Ethyltoluene 0.08 0.09 0.08
1,3,5-Trimethylbenzene 0.06 0.06 0.06
o-Ethyttoluene 0.06 0.06 0.05
b-Pinene 0.14 0.08 0.09
1,2,4-Trimethylbenzene ND ND ND
1-Decene 0.16 0.20 0.18
n-Decane 0.10 0.10 0.08
1,2,3-Trimethylbenzene 0.03 0.04 0.04
m-Diethylbenzene 0.07 0.05 0.08
p-Diethylbenzene 0.16 0.10 0.20
1-Undecene 0.02 0.02 0.02
n-Undecane 0.19 0.11 0.12
1-Dodeoene ND ND 0.01
n-Dodecane 0.10 0.01 0.04
1-Tridecene ND 0.003 0.01
n-Tridecane 0.01 0.01 0.01
TNMOC (speciated), ppbv 51.49 29.22 24.59
TNMOC (w/unknowns), ppbC 405.95 245.53 267.43
# The QC recovery for n-Undecane was outside of criteria on 1/11/99.
1 of 10
-------
SNMOC OPTION REPORT
SITE CODE: BRVT
Brattleboro, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1 -Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2.2-Dimethyl butane
Cyclopentene
4-Methyl-1 -pentene
Cyclopentane
2,3-Oimethylbutane
2-Methylpentane
3-Methylpentane
2-Methyl-1 -pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimethylpentane
3-Methylhexane
1-Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Etnylbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropyl benzene
a-Pinene
n-Propylbenzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethyl benzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethyl benzene
1-Decene
n-Decane
1,2,3-Trimethylbenzene
m-Diethylbenzene
p-Diethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
15137
10/20/98
12/6/98
1.33
1.05
1.93
0.57
3.42
0.03
1.10
0.24
0.05
2.60
0.21
0.21
0.04
4.20
0.12
0.18
0.74
0.09
0.19
0.13
0.20
0.19
0.03
ND
0.10
0.32
0.42
0.26
0.03
0.02
ND
0.28
0.02
0.01
0.17
0.10
0.45
0.18
0.14
0.13
0.15
ND
0.20
0.12
0.09
0.03
0.09
0.61
0.06
0.05
0.01
0.07
0.42
0.69
0.16
0.27
ND
0.07
0.06
0.05
0.08
0.16
0.09
0.08
0.07
0.07
ND
0.21
0.08
0.13
0.09
0.14
0.02
0.10
ND
0.01
ND
0.003
15155
11/1/98
11/11/98
0.72
0.63
1.57
0.37
1.92
ND
0.28
0.13
0.02
0.47
0.11
0.13
ND
2.03
0.07
0.04
0.22
0.09
0.08
0.09
0.02
0.11
0.02
ND
0.07
0.15
0.16
0.12
0.02
0.02
ND
0.11
ND
ND
0.09
0.09
0.31
0.36
0.09
0.12
0.09
ND
0.09
0.07
0.07
0.03
0.06
0.34
0.05
0.06
ND
0.07
0.35
0.43
0.13
0.20
ND
0.06
0.06
0.004
0.06
0.11
0.07
0.04
0.05
0.05
ND
0.12
0.06
0.08
0.11
0.19
0.03
0.14
0.004
0.01
ND
ND
15195
11/13/98
12/1/98
2.51
1.84
2.55
0.92
4.15
0.05
1.88
0.42
0.13
3.79
0.38
0.35
0.05
4.78
0.22
0.29
1.03
0.12
0.31
0.21
0.36
.0.28 ,
0.08
0.01
0.16
0.46
0.61
0.40
0.05
0.03
ND
0.35
0.03
0.01
0.23
0.13
0.64
0.97
0.22
0.19
0.21
ND
0.32
0.16
0.13
0.05
0.12
1.06
0.08
0.08
0.01
0.09
0.49
1.00
0.12
0.35
ND
0.06
0.07
0.07
0.08
0.23
0.12
0.09
0.09
0.02
ND
0.22
0.08
0.14
0.10
0.11
0.02
0.08
ND
0.005
ND
ND
15237
11/25/98
12/8/98
3.36
2.42
3.03
1.07
9.21
0.06
1.03
0.37
0.15
1.75
0.22
0.22
0.03
4.02
0.14
0.18
0.78
0.13
0.20
0.15
0.21
0.20
0.08
ND
0.13
0.37
0.52
0.31
0.03
0.02
ND
0.32
0.04
0.02
0.21
0.11
0.71
0.23
0.18
0.15
0.21
ND
0.26
0.19
0.13
0.05
0.12
1.24
0.08
0.09
0.01
0.11
0.53
1.03
0.13
0.39
ND
0.06
0.06
0.13
0.09
0.22
0.12
0.11
0.09
0.03
ND
0.23
0.09
0.10
0.09
0.19
0.03
0.06
0.004
0.01
ND
ND
TNMOC (speciated), ppbv 26.02
TNMOC (w/ unknowns), ppbC 260.53
# The QC recovery for n-Undecan
14.10
199.76
37.06
284.89
38.64
289.68
2 of 10
-------
SNMOC OPTION REPORT
SITE CODE: BRVT
Brattleboro, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1 -Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-M9thyl-2-butene
2,2-Dimethylbutane
Cyclopentene
4-Methyl-1 -pentene
Cyclopentane
2,3-Dimethylbutane
2-Methylpentane
3-Methylpentane
2-Methyl-1 -pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimethylpentane
3-Methylhexane
1-Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethylbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropyl benzene
a-Pinene
n-Propylbenzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethylbenzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethylbenzene
1-Decene
n-Decane
1,2,3-Trimethylbenzene
m-Diethylbenzene
p-Diethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
15251
12/7/98
12/22/98
2.25
1.69
3.18
0.76
3.94
0.02
4.94
0.33
0.08
2.40
0.21
0.22
0.02
10.60
0.11
0.12
1.30
0.11
0.17
0.13
0.16
0.20
0.06
ND
0.15
0.58
0.70
0.70
0.03
0.02
ND
1.50
0.02
0.01
0.63
0.14
0.53
23.94
0.24
0.17
0.25
ND
0.27
0.21
0.16
0.07
0.11
1.26
0.10
0.10
0.01
0.13
0.40
0.76
0.15
0.38
ND
0.09
0.06
0.10
0.08
0.18
0.10
0.08
0.07
0.09
0.22
ND
0.10
0.10
0.09
0.20
0.04
0.15
ND
0.07
ND
0.04
15282
12/19/98
1/12/99
3.85
3.13
3.21
1.14
4.79
0.03
2.31
0.59
0.13
3.77
0.43
0.37
ND
4.13
0.17
0.19
0.95
0.12
0.22
0.17
0.24
0.22
0.10
ND
0.15
0.53
0.57
0.38
0.03
0.02
ND
0.37
0.02
0.01
0.25
0.14
0.83
2.76
0.35
0.19
0.26
ND
0.29
0.19
0.15
0.06
0.12
1.18
0.09
0.08
0.01
0.11
0.50
1.00
0.15
0.38
ND
0.09
0.07
0.23
0.11
0.24
0.12
0.12
0.09
0.06
0.31
ND
0.10
0.13
0.10
0.17
0.05
0.12
ND
0.02
ND
1.45
15304
12/21/98
1/12/99
4.36
2.76
3.35
1.27
8.90
0.03
1.66
0.80
0.16
3.29
0.29
0.28
ND
4.24
0.14
0.17
0.89
0.13
0.19
0.15
0.20
0.18
0.02
0.004
0.14
0.34
0.53
0.35
0.04
0.03
ND
0.38
0.02
0.02
0.27
0.12
0.75
5.87
0.25
0.17
0.27
ND
0.28
0.23
0.16
0.06
0.12
1.34
0.08
0.09
0.01
0.12
0.56
0.99
0.12
0.39
ND
0.10
0.06
0.02
0.11
0.27
0.12
0.11
0.09
0.03
0.26
ND
0.09
0.05
0.07
0.13
0.03
0.09
ND
0.01
ND
ND
15318
1/12/99
1/22/99
3.98
3.18
3.69
1.19
7.61
0.08
1.80
2.88
0.16
4.30
0.27
0.27
0.04
3.98
0.12
0.15
0.93
0.11
0.18
0.13
0.21
0.20
0.08
0.01
0.13
0.44
0.60
0.42
0.03
0.02
ND
0.38
0.03
0.02
0.27
0.14
0.78
0.66
0.22
0.20
0.26
ND
0.37
0.21
0.15
0.07
0.14
1.36
0.10
0.09
0.01
0.12
0.53
1.06
0.13
0.43
ND
0.06
0.06
0.04
0.10
0.25
0.12
0.12
0.09
0.01
0.31
ND
0.07
0.11
0.08
0.13
0.01
0.09
ND
0.01
ND
0.01
TNMOC (speciated), ppbv 68.60
TNMOC (w/ unknowns), ppbC 475.52
# The QC recovery for n-Undecan
45.03
352.91
3 of 10
49.22
345.01
46.55
316.07
-------
SNMOC OPTION REPORT
SITE CODE: BRVT
Brattleboro, VT
Reported in ppbv
Sanple No.:
Sannpling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1-Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethylbutane
Cyclopentene
4-Methyl-1-pentene
Cyclopentane
2,3-Dimethytbutane
2-Methylpentane
3-Methylpentane
2-Methyl-1 -pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Oimethylpentane
Benzene
Cyclohexane
2-Mettiylhexane
2,3-Dimethylpentane
3-Methylhexane
1-Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethylbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropyl benzene
a-Pinene
n-Propylbenzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethyl benzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethyl benzene
1-Decene
n-Oecane
1,2,3-Trimethylbenzene
m-Diethylbenzene
p-Diethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
15349D1
1/24/99
2/2/99
3.25
2.28
2.87
0.95
8.51
0.03
1.43
0.37
0.14
2.91
0.24
0.23
0.23
4.17
0.13
0.11
1.42
0.14
0.18
0.13
0.17
0.20
0.08
ND
0.14
0.41
0.53
0.38
0.03
0.03
ND
0.39
0.02
0.02
0.28
0.14
0.65
33.54
0.20
0.18
0.23
ND
0.32
0.17
0.13
0.06
0.13
1.13
0.08
0.08
ND
0.10
0.36
0.83
0.16
0.34
ND
0.07
0.05
0.21
0.10
0.24
0.14
0.11
0.10
0.07
0.30
ND
0.09
0.11
0.08
0.09
0.01
0.15
ND
0.04
0.004
1.11
1S349R1
1/24/99
2/9/99
3.14
2.12
2.91
0.94
8.06
0.05
1.35
0.35
0.13
2.76
0.22
0.22
0.36
4.17
0.12
0.12
1.34
0.13
0.17
0.13
0.15
0.18
0.09
ND
0.13
0.39
0.53
0.36
0.03
0.03
ND
0.41
0.02
0.02
0.26
0.12
0.60
31.68
0.25
0.17
0.22
ND
0.30
0.18
0.12
0.07
0.12
1.08
0.08
0.07
0.01
0.10
0.35
0.79
0.17
0.34
ND
0.06
0.05
0.22
0.08
0.21
0.13
0.12
0.09
0.07
0.28
ND
0.07
0.07
0.08
0.11
0.03
0.13
ND
0.04
0.90
ND
1S351D2
1/24/99
2/2/99
3.37
2.25
3.06
1.00
8.61
0.05
1.46
0.72
0.09
3.02
0.22
0.25
0.04
3.69
0.03
0.10
1.47
0.02
0.16
0.10
0.04
0.19
0.31
0.01
0.13
0.41
0.54
0.36
0.02
0.02
ND
0.38
0.02
0.01
0.24
0.13
0.62
27.38
0.27
0.20
0.23
0.05
0.33
0.17
0.13
0.07
0.13
1.09
0.09
0.09
0.02
0.10
0.29
0.71
0.10
0.30
0.02
0.08
0.05
0.08
0.08
0.23
0.13
0.11
0.10
0.04
0.25
ND
0.07
0.05
0.08
0.07
1.68
0.07
0.04
003
ND
0.03
15351R2
1/24/99
2/9/99
3.20
2.13
2.83
0.95
8.17
0.05
1.38
0.75
0.05
2.91
0.22
0.20
0.03
3.68
0.14
0.11
1.41
0.01
0.14
0.08
0.04
0.18
0.46
ND
0.13
0.36
0.48
0.36
0.02
0.03
ND
0.36
0.02
ND
0.25
0.12
0.59
26.03
0.21
0.17
0.22
ND
0.31
0.16
0.12
0.07
0.12
1.03
0.08
0.09
0.01
0.10
0.28
0.66
0.11
0.28
0.02
0.07
0.05
0.03
0.08
0.21
0.13
0.10
0.11
0.05
0.28
ND
0.09
0.06
0.07
0.06
2.04
0.07
ND
0.03
0.003
0.03
TNMOC (speciated), ppbv 74.32
TNMOC (w/ unknowns), ppbC 462.71
# The QC recovery for n-Undecan
70.92
442.29
68.17
468.18
65.46
468.26
4 of 10
-------
SNMOC OPTION REPORT
SITE CODE: BRVT
Brattleboro, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1 -Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethylbutane
Cyclopentene
4-Methyl-1 -pentene
Cyclopentane
2,3-Dimethyl butane
2-Methylpentane
3-Methylpentane
2-MethyM-pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimethylpentane
3-Methylhexane
1-Heptane
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethylbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropyl benzene
a-Pinene
n-Propyl benzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethylbenzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethylbenzene
1-Decene
n-Decane
1,2,3-Trimethylbenzene
m-Diethyl benzene
p-Diethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
15413
2/5/99
2/23/99
1.32
1.05
2.45
0.49
3.01
ND
0.45
0.41
0.07
0.93
0.08
0.11
ND
2.33
0.06
0.04
0.35
0.07
0.07
0.07
0.04
0.10
0.10
ND
0.06
0.15
0.21
0.16
0.02
0.01
ND
0.17
ND
ND
0.11
0.08
0.44
0.21
0.11
0.11
0.10
ND
0.13
0.08
0.07
0.02
0.07
0.47
0.05
0.05
0.005
0.06
0.38
0.61
0.18
0.21
ND
0.05
0.05
0.05
0.08
0.12
0.07
0.07
0.05
0.07
0.18
ND
0.05
0.07
0.08
0.17
0.04
0.09
ND
0.01
ND
0.02
15443
2/17/99
3/4/99
1.85
1.28
1.35
0.50
4.17
0.02
0.62
0.19
0.07
1.09
0.12
0.10
0.01
1.60
0.05
0.07
0.35
0.03
0.06
0.04
0.10
0.06
0.06
0.004
0.04
0.18
0.27
0.16
0.01
0.02
ND
0.18
0.02
0.07
0.11
0.04
0.36
0.14
0.11
0.06
0.12
ND
0.15
0.10
0.05
0.04
0.05
0.73
0.04
0.04
0.005
0.05
0.21
0.48
0.03
0.19
ND
0.02
0.01
0.08
0.03
0.12
0.04
0.05
0.03
0.02
0.14
ND
0.03
0.02
0.02
0.05
0.01
0.04
ND
0.01
ND
0.01
15483
3/1/99
3/11/99
0.97
0.79
1.09
0.32
2.27
ND
1.21
0.41
0.04
1.67
0.31
0.25
0.02
1.66
0.06
0.09
0.37
0.03
0.10
0.07
0.11
0.06
0.04
0.00
0.05
0.15
0.23
0.15
0.01
0.01
ND
0.15
0.01
ND
0.08
0.04
0.24
0.10
0.08
0.06
0.08
ND
0.09
0.06
0.04
0.02
0.04
0.37
0.03
0.03
0.00
0.03
0.06
0.31
0.03
0.14
ND
0.03
0.02
0.04
0.03
0.07
0.04
0.04
0.03
0.02
0.10
ND
0.03
0.04
0.03
0.06
0.01
0.04
ND
0.008
ND
0.00
15547
3/13/99
3/24/99
1.48
1.19
2.45
0.93
3.54
ND
0.44
0.59
0.07
0.76
0.10
0.13
ND
6.63
0.10
0.11
0.38
0.08
0.08
0.08
0.10
0.13
0.02
ND
0.05
0.17
0.23
0.17
0.02
0.03
ND
0.15
ND
ND
0.13
0.08
0.53
0.19
0.43
0.11
0.13
0.03
0.13
0.07
0.07
0.05
0.11
0.48
0.06
0.07
0.02
0.08
0.91
1.33
0.20
0.58
ND
0.14
0.09
ND
0.13
0.26
0.07
0.06
1.54
0.21
0.24
ND
0.26
0.21
0.23
0.56
0.17
0.33
0.010
0.02
ND
0.01
TNMOC (speciated), ppbv 19.27
TNMOC (w/ unknowns), ppbC 216.25
# The QC recovery for n-Undecan
18.58
214.83
15.25
115.19
30.56
761.45
5 of 10
-------
SNMOC OPTION REPORT
SITE CODE: BRVT
Brattleboro, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1 -Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Oimethylbutane
Cyclopentene
4-Methyl-1-pentene
Cyclopentane
2,3-Dimethylbutane
2-Methylpentane
3-Methylpentane
2-Methyl-1 -pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimethylpentane
3-Methylhexane
1-Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimettiylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethylbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropylbenzene
a-Pinene
n-Propylbenzene
m-Ettiyltoluene
p-Ethyltoluene
1,3,5-Trimethylbenzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethylbenzene
1-Decene
n-Decane
1,2,3-Trimethylbenzene
m-Diethyl benzene
p-Diethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
1SS87D1
3/25/99
4/13/99
1.99
1.39
3.22
0.77
5.94
ND
0.93
0.28
0.07
1.43
0.24
0.22
0.04
3.14
0.09
0.19
0.50
0.10
0.14
0.14
0.13
0.14
0.08
ND
0.09
0.28
0.40
0.22
0.02
0.02
ND
0.22
ND
ND
0.17
0.10
0.43
0.13
0.17
0.15
0.14
0.01
0.15
0.10
0.09
0.01
0.10
0.68
0.08
0.07
0.01
0.09
0.94
0.73
0.16
0.25
ND
0.06
0.06
0.12
0.07
0.17
0.10
0.06
0.06
0.05
0.18
ND
0.09
0.10
0.08
0.13
0.02
0.13
0.01
0.02
ND
0.00
15587R1
3/25/99
4/13/99
2.05
1.38
3.29
0.75
6.16
ND
0.90
0.27
0.05
1.45
0.21
0.22
0.03
3.12
0.09
0.13
0.47
0.11
0.13
0.11
0.12
0.12
0.03
ND
0.09
0.24
0.35
0.23
0.02
0.02
ND
0.24
ND
ND
0.18
0.10
0.42
0.13
0.16
0.14
0.14
ND
0.15
0.11
0.09
0.02
0.08
0.67
0.06
0.07
ND
0.09
0.31
0.68
0.16
0.24
ND
0.06
0.07
0.11
0.06
0.16
0.08
0.06
0.06
0.05
0.16
ND
0.08
0.09
0.08
0.12
0.04
0.12
0.00
0.022
ND
0.01
15589D2
3/25/99
4/13/99
2.14
1.58
2.83
0.72
5.63
ND
0.81
0.31
0.08
1.29
0.23
0.25
ND
3.19
0.11
0.15
0.47
0.11
0.14
0.12
0.12
0.14
0.03
ND
0.08
0.30
0.33
0.23
0.02
0.03
ND
0.24
ND
ND
0.19
0.11
0.45
0.14
0.29
0.16
0.14
0.02
0.17
0.12
0.11
0.02
0.10
0.69
0.07
0.07
0.01
0.10
1.00
0.79
0.11
0.24
ND
0.09
0.06
0.11
0.05
0.17
0.08
0.07
0.07
ND
0.17
ND
0.07
0.05
0.08
0.13
0.02
0.08
ND
0.02
ND
0.01
15589R2
3/25/99
4/13/99
2.19
1.53
2.76
0.73
5.78
ND
0.83
0.26
0.08
1.32
0.23
0.23
ND
3.22
0.11
0.14
0.50
0.09
0.13
0.12
0.13
0.13
0.03
ND
0.08
0.27
0.32
0.22
0.02
0.03
ND
0.22
0.02
ND
0.18
0.10
0.47
0.15
0.29
0.15
0.14
0.03
0.16
0.10
0.09
0.03
0.09
0.67
0.06
0.07
0.01
0.09
0.37
0.77
0.09
0.26
0.02
0.08
0.05
0.14
0.08
0.18
0.08
0.07
0.06
0.01
0.17
ND
0.08
0.04
0.04
0.08
0.02
0.06
ND
0.01
ND
ND
TNMOC (speciated), ppbv 28.67
TNMOC (w/ unknowns), ppbC 252.27
# The QC recovery for n-Undecan
27.77
245.44
28.11
238.58
27.40
245.12
6 of 10
-------
SNMOC OPTION REPORT
SITE CODE: BRVT
Brattleboro, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1-Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethylbutane
Cyclopentene
4-Methyl-1-pentene
Cyclopentane
2,3-Dimethylbutane
2-Methylpentane
3-Methylpentane
2-Methyl-1-pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimethylpentane
3-Methylhexane
1-Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2.3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethylbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropylbenzene
a-Pinene
n-Propylbenzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethylbenzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethyl benzene
1-Decene
n-Decane
1,2,3-Trimethylbenzene
m-Diethylbenzene
p-Diethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
15656
4/6/99
5/10/99
1.34
1.15
2.14
0.54
4.65
ND
0.93
0.23
0.04
1.48
0.25
0.24
0.03
2.76
0.11
0.13
0.49
O.OB
0.14
0.12
0.13
0.15
0.04
ND
0.08
0.29
0.37
0.23
0.02
0.03
ND
0.24
0.01
ND
0.17
0.09
0.36
1.07
0.30
0.15
0.13
0.03
0.13
0.10
0.09
0.03
0.08
0.69
0.07
0.07
0.01
0.10
0.47
0.67
0.18
0.23
ND
0.09
0.07
0.18
0.07
0.14
0.06
0.05
0.05
0.07
0.14
ND
0.09
0.11
0.08
0.12
0.03
0.11
0.00
0.015
ND
0.00
15826
5/12/99
VOID
15828
5/12/99
VOID
15789
5/18/99
6/7/99
1.46
0.91
1.82
0.60
4.37
0.02
0.69
0.26
0.05
1.36
0.20
0.22
0.04
5.05
0.15
0.15
0.96
0.11
0.21
ND
0.15
0.23
0.07
ND
0.12
0.42
0.60
0.29
0.03
0.04
ND
0.29
0.01
0.01
0.20
0.10
0.33
0.46
0.27
0.17
0.17
0.03
0.18
0.15
0.14
0.04
0.09
0.70
0.05
0.06
ND
0.08
0.40
0.54
0.23
0.15
ND
0.07
0.06
0.25
0.09
0.16
0.08
0.06
0.06
0.11
0.15
ND
0.07
0.04
0.07
0.13
0.04
0.16
0.01
0.01
0.00
0.01
TNMOC (speciated), ppbv 25.16
TNMOC (w/ unknowns), ppbC 275.51
# The QC recovery for n-Undecan
27.08
275.90
7 of 10
-------
SNMOC OPTION REPORT
SITE CODE: BRVT
Brattleboro, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethytene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1-Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyt-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethylbutane
Cyclopentene
4-Methyl-1-pentene
Cyclopentane
2.3-Oimethylbutane
2-Melhylpentane
3-Methylpentane
2-Methyl-1-pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Oimethylpentane
3-Methylhexane
1-Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethylbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
l-Nonene
n-Nonane
Isopropytbenzene
a-Pinene
n-Propyl benzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethylbenzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethyl benzene
1-Decene
n-Decane
1,2,3-Trimethylbenzene
m-Diethyl benzene
p-Diethyl benzene
1-Undecene
n-Undecane
1-Dodecene
n-Oodecane
1-Tridecene
n-Tridecane
15836
5/30/99
6/17/99
1.48
0.89
2.68
0.60
6.16
ND
0.37
0.21
0.06
0.84
0.11
0.15
0.02
2.45
0.11
0.09
0.60
0.49
0.12
0.10
0.09
0.15
0.11
ND
0.10
0.14
0.42
0.21
0.02
0.03
ND
0.28
ND
ND
0.18
0.10
0.33
0.19
0.29
0.17
0.14
0.02
0.16
0.16
0.08
0.04
0.08
0.68
0.07
0.07
ND
0.13
0.57
0.80
0.26
0.28
ND
0.11
0.06
0.26
0.10
0.22
0.08
0.06
0.06
0.23
0.15
ND
0.11
0.09
0.07
0.17
0.08
0.16
ND
0.02
ND
0.01
15838
6/5/99
6/17/99
1.11
0.78
1.57
0.42
3.33
ND
0.63
0.18
0.04
1.20
0.16
0.19
0.03
1.78
0.11
0.10
0.73
0.34
0.16
0.13
0.14
0.17
0.03
ND
0.11
0.14
0.45
0.21
0.03
0.02
ND
0.21
ND
ND
0.15
0.09
0.26
0.57
0.25
0.14
0.12
ND
0.16
0.09
0.07
0.02
0.07
0.56
0.04
0.05
0.01
0.07
0.41
0.34
0.20
0.13
ND
0.07
0.07
0.02
0.05
0.14
0.07
0.06
0.05
0.05
0.12
ND
0.10
0.08
0.07
0.19
0.03
0.07
ND
0.009
ND
0.01
15919
6/17/99
6/29/99
1.31
0.88
1.52
0.49
2.64
ND
1.07
0.30
0.05
2.43
0.34
0.34
0.07
3.21
0.28
0.24
1.38
0.44
0.29
0.20
0.33
0.24
0.07
ND
0.17
6.88
0.69
0.35
0.05
0.03
ND
6.95
0.04
0.02
0.19
0.13
0.35
0.88
4.41
0.14
0.17
0.25
0.18
0.13
0.11
0.04
3.16
6.80
0.08
2.89
0.19
0.08
0.43
0.69
0.23
0.17
0.11
0.07
0.24
0.14
0.08
0.15
0.07
0.06
1.36
0.13
0.14
ND
0.07
0.08
0.09
0.43
0.10
0.22
0.04
0.04
0.01
0.01
16022
6/29/99
7/20/99
1.60
1.12
1.95
0.68
3.31
ND
0.86
0.28
0.07
1.86
0.25
0.27
0.05
2.41
0.20
0.20
1.22
0.96
0.25
0.19
0.27
0.27
0.17
ND
0.16
0.64
0.68
0.38
0.03
0.03
ND
0.36
0.02
0.01
0.23
0.13
0.46
1.45
0.34
0.24
0.25
ND
0.26
0.18
0.13
0.06
0.11
0.99
0.07
0.07
0.01
0.09
0.50
0.81
0.22
0.34
ND
0.08
0.07
0.10
0.10
0.18
0.10
0.09
0.11
0.20
0.18
ND
0.10
0.11
0.14
0.22
0.05
0.14
0.01
0.02
ND
0.01
TNMOC (speciated), ppbv 25.91
TNMOC (w/ unknowns), ppbC 313.46
# The QC recovery for n-Undecan
19.56
263.60
58.65
493.31
29.65
329.87
8 of 10
-------
SNMOC OPTION REPORT
SITE CODE: BRVT
Brattleboro, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1 -Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butane
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethylbutane
Cyclopentene
4-Methyl-1-pentene
Cyclopentane
2,3-Dimethylbutane
2-Methylpentane
3-Methylpentane
2-Methy1-1-pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methythexane
2,3-Dimethylpentane
3-Methylhexane
1-Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethylbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropylbenzene
a-Pinene
n-Propylbenzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethyl benzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethylbenzene
1-Decene
n-Decane
1,2,3-Trimethylbenzene
m-Oiethylbenzene
p-Diethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Oodecane
1-Tridecene
n-Tridecane
16269
7/17/99
8/10/99
1.68
1.25
2.14
0.60
5.08
ND
0.73
0.33
0.06
1.20
0.25
0.30
0.05
1.97
0.17
0.19
0.85
1.14
0.25
0.17
0.23
0.25
0.21
ND
0.12
0.20
0.63
0.34
0.03
0.04
ND
0.33
0.03
0.01
0.21
0.11
0.45
0.10
0.24
0.15
0.15
ND
0.19
0.13
0.11
0.07
0.09
0.79
0.07
0.06
0.03
0.08
0.15
0.40
0.31
0.16
0.03
0.06
0.07
0.31
0.08
0.23
0.09
0.06
0.10
0.40
0.23
ND
0.09
0.10
0.28
0.19
0.06
0.19
0.02
0.021
0.01
0.02
16252
7/23/99
8/10/99
1.68
1.13
1.61
0.60
3.47
ND
0.74
0.40
0.06
1.22
0.28
0.29
0.05
2.12
0.17
0.19
0.78
0.86
0.23
0.16
0.25
0.21
0.20
ND
0.11
0.19
0.71
0.32
0.03
0.03
ND
0.29
0.03
0.02
0.20
0.13
0.44
0.18
0.26
0.20
0.15
ND
0.25
0.11
0.09
0.06
0.10
0.79
0.05
0.05
0.01
0.07
0.15
0.38
0.20
0.16
0.02
0.06
0.04
0.20
0.06
0.18
0.09
0.06
0.09
0.15
0.19
ND
0.11
0.11
0.14
0.10
0.05
0.17
0.01
0.02
ND
0.01
16283
8/4/99
8/16/99
1.07
0.67
i.15
0.42
3.31
ND
0.78
0.29
0.04
1.38
0.31
0.32
0.06
2.14
0.16
0.18
0.83
0.69
0.26
0.18
0.26
0.19
0.12
ND
0.13
0.19
0.52
0.30
0.03
0.04
ND
0.24
0.03
ND
0.18
0.10
0.32
0.18
0.24
0.17
0.10
0.03
0.15
0.10
0.10
0.04
0.07
0.61
0.06
0.05
0.02
0.06
0.10
0.24
0.12
0.10
0.02
0.06
0.06
0.09
0.06
0.13
0.07
0.06
0.07
0.17
0.15
ND
0.09
O.OB
0.23
0.14
0.08
0.24
0.01
0.02
0.00
0.01
16496
8/16/99
9/3/99
1.00
0.64
1.06
0.42
2.27
ND
0.41
0.20
0.03
0.72
0.16
0.19
0.03
4.42
0.10
0.10
0.84
0.47
0.14
0.13
0.12
0.14
0.06
ND
0.11
0.15
0.43
0.25
0.02
0.02
ND
0.18
0.02
ND
0.11
0.09
0.30
0.15
0.21
0.16
0.12
0.02
0.14
0.09
0.10
ND
0.06
0.49
0.05
0.05
0.02
0.06
0.12
0.24
0.21
0.12
0.02
0.05
0.07
0.16
0.07
0.15
0.07
0.05
0.06
0.16
0.11
ND
0.08
0.08
0.10
0.13
0.02
0.17
ND
0.01
ND
0.01
TNMOC (speciated), ppbv 27.49
TNMOC (w/ unknowns), ppbC 245.68
# The QC recover/ for n-Undecan
24.35
220.90
21.27
179.54
19.29
159.10
9 of 10
-------
SNMOC OPTION REPORT
SITE CODE: BRVT
Brattleboro, VT
Reported in ppbv
Sample No.: 16611 16614 16803 16903
Sampling Date: 8/28/99 9/3/99 9/9/99 9/21/99
Analysis Date: VOID 9/14/99 10/6/99 10/11/99
Compound
Ethylene 2.44 1.71 1.71
Acetylene 1.36 1.34 1.30
Ethane 1.53 2.34 1.40
Propylene 0.80 0.58 0.60
Propane 6.46 4.31 3.86
Propyne ND ND ND
Isobutane 0.40 0.79 0.46
lsobutene/1-Butene 0.27 0.26 0.32
1,3-Butadiene 0.09 0.07 0.06
n-Butane 0.63 1.54 0.79
trans-2-Butene 0.11 0.21 0.19
cis-2-Butene 0.16 0.24 0.22
3-MethyM-butene 0.02 0.05 0.04
Isopentane 1.20 2.58 1.31
1-Pentene 0.10 0.14 0.12
2-Methyl-1-butene 0.10 0.19 0.12
n-Pentane 0.62 1.08 0.65
Isoprene 1.31 0.69 0.15
trans-2-Pentene 0.15 0.25 0.17
cis-2-Pentene 0.12 0.17 0.13
2-Methyl-2-butene 0.12 0.25 0.18
2,2-Dimethylbutane 0.15 _•-_ 0.19 0.14
Cyclopentene 0.11 0.09 0.02
4-Methyl-1-pentene ND ND 0.01
Cyclopentane 0.10 0.14 0.10
2,3-Dimethylbutane 0.16 0.21 0.15
2-Methylpentane 0.49 0.82 0.46
3-Methylpentane 0.25 0.38 0.25
2-Methyl-1-pentene 0.03 0.04 0.02
1-Hexene 0.04 0.02 0.03
2-Ethyl-1-butene 0.23 0.32 0.21
n-Hexane ND ND ND
trans-2-Hexene 0.02 0.03 0.03
cis-2-Hexene 0.01 0.01 0.01
Methylcyclopentane 0.16 0.20 0.14
2,4-Dimethylpentane 0.13 0.12 0.11
Benzene 0.45 0.43 0.37
Cyclohexane 0.32 1.08 0.10
2-Methylhexane 0.28 0.24 0.15
2,3-Dimethylpentane 0.21 0.20 0.14
3-Methylhexane 0.15 0.18 0.13
1-Heptene 0.04 0.05 0.04
2.2,4-Trimethylpentane 0.21 0.23 0.19
n-Heptane 0.14 0.14 0.11
Methylcyclohexane 0.10 0.12 0.10
2.2,3-Trimethylpentane 0.04 0.05 0.03
2,3,4-Trimethylpentane 0.09 0.09 0.09
Toluene 0.83 0.97 0.68
2-Methylheptane 0.05 0.05 0.05
3-Methylheptane 0.06 0.06 0.05
1-Ootene 0.02 0.01 0.01
n-Octane 0.08 0.07 0.07
Ethylbenzene 0.16 0.15 0.13
m-Xylene/p-Xylene 0.42 0.37 0.34
Styrene 0.26 0.15 0.14
o-Xylene 0.19 0.17 0.14
1-Nonene 0.03 ND 0.02
n-Nonane 0.07 0.05 0.05
Isopropylbenzene 0.07 0.06 0.05
a-Pinene 0.29 0.16 0.33
n-Propylbenzene 0.08 0.07 0.07
m-Ethyltoluene 0.25 0.19 0.14
p-Ethyltoluene 0.08 0.09 0.07
1,3,5-Trimethylbenzene 0.08 0.08 0.05
o-Ethyltoluene 0.10 0.08 0.06
b-Pinene 0.29 0.17 0.14
1,2,4-Trimethylbenzene ND ND ND
1-Decene 0.17 0.17 0.15
n-Decane 0.09 0.06 0.08
1,2,3-Trimethylbenzene 0.12 0.06 0.10
m-Diethylbenzene 0.22 0.21 0.23
p-Diethylbenzene 0.17 0.15 0.15
1-Undecene . 0.07 0.06 0.07
n-Undecane 0.25 0.22 0.17
1-Dodecene 0.03 0.02 0.01
n-Dodecane 0.02 0.05 0.01
1-Tridecene 0.00 0.00 0.00
n-Tridecane 0.02 0.01 0.01
TNMOC (speciated), ppbv 26.44 28.14 20.47
TNMOC (w/unknowns), ppbC 208.81 243.22 197.97
# The QC recovery for n-Undecan
10 of 10
-------
SNMOC OPTION REPORT
SITE CODE: BUVT
Burlington, VT
Reported In ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1-Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethylbutane
Cyclopentene
4-Methyl-1-pentene
Cyclopentane
2,3-Dimethylbutane
2-Methylpentane
3-Methytpentane
2-Methyl-1-pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimethylpentane
3-Methylhexane
1-Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethylbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropylbenzene
a-Pinene
n-Propylbenzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethylbenzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethylbenzene
1-Decene
n-Decane
1,2,3-Trimethylbenzene
m-Diethylbenzene
p-Diethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
14818
9/14/98
10/14/98
3.01
2.03
2.26
1.10
2.36
0.06
0.93
0.38
0.16
1.46
0.26
0.26
0.05
6.10
0.17
0.23
1.14
0.20
0.27
0.17
0.31
0.32
0.15
0.02
0.16
0.55
0.77
0.48
0.05
0.03
NO
0.49
0.04
0.03
0.31
0.15
0.86
44.35
0.24
0.19
0.27
NO
0.40
0.18
0.14
0.08
0.14
1.84
0.08
0.09
0.01
0.10
0.28
0.87
0.13
0.34
0.02
0.07
0.06
0.06
0.08
0.26
0.13
0.13
0.10
0.08
0.36
NO
0.08
0.08
0.10
0.05
0.03
0.06
0.005
0.02
ND
0.004
15083
9/26/98
10/22/98
2.52
1.69
3.34
0.86
2.26
0.06
0.72
0.31
0.12
1.84
0.24
0.22
0.04
5.42
0.13
0.18
0.94
0.13
0.23
0.16
0.28
0.26
0.11
0.01
0.12
0.49
0.64
0.37
0.03
0.03
NO
0.32
0.03
0.02
0.24
0.11
0.73
0.25
0.20
0.16
0.21
ND
0.31
0.14
0.10
0.07
0.11
1.36
0.07
0.07
0.03
0.10
0.23
0.68
0.14
0.27
0.02
0.06
0.06
0.01
0.07
0.21
0.11
0.10
0.09
0.08
0.31
ND
0.07
0.11
0.06
0.04
0.03
0.12
0.01
0.02
0.01
0.01
15107
10/8/98
10/22/98
3.51
2.15
2.35
1.11
1.55
0.05
1.02
0.41
0.18
2.16
0.28
0.25
0.06
4.17
0.16
0.25
0.99
0.14
0.28
0.18
0.34
0.24
0.06
0.01
0.13
0.51
0.66
0.41
0.04
0.03
ND
0.38
0.05
0.03
0.26
0.12
0.95
3.85
0.25
0.18
0.23
ND
0.37
0.18
0.12
0.08
0.15
1.63
0.09
0.08
0.01
0.10
0.31
0.96
0.15
0.36
0.01
0.07
0.05
0.02
0.10
0.29
0.14
0.13
0.11
0.08
0.41
ND
0.10
0.13
0.13
0.09
0.04
0.20
0.01
0.04
ND
0.01
16147
10/16/98
12/7/98
3.46
2.02
2.84
1.21
2.31
0.05
1.89
0.44
0.16
3.44
0.31
0.30
0.04
6.72
0.19
0.26
1.06
0.15
0.29
0.20
0.39
0.25
0.13
0.01
0.14
0.43
0.75
0.40
0.06
0.04
ND
0.39
0.04
0.03
0.28
0.13
0.92
1.04
0.25
0.22
0.24
ND
0.38
0.17
0.12
0.08
0.15
1.39
0.08
0.09
0.01
0.11
0.25
0.77
0.22
0.32
0.02
0.08
0.06
ND
0.11
0.29
0.15
0.16
0.14
0.05
0.43
ND
0.12
0.11
0.13
0.10
0.04
0.16
0.004
0.02
ND
0.004
TNMOC (speciated), ppbv
TNMOC (w/ unknowns), ppbC
78.82
486.70
31.28
190.03
36.73
237.71
39.82
243.15
# - The QC recovery for n-Undecane is outside of QC criteria on 1/11/99
1of10
-------
SNMOC OPTION REPORT
SITE CODE: BUVT
Burlington, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1-Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethylbutane
Cyclopentene
4-Methyl-1-pentene
Cyclopentane
2,3-Dimethylbutane
2-Methylpentane
3-Methylpentane
2-Methyl-1-pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimettiylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimethylpentane
3-Methylhexane
1-Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2.2,3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethylbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropylbenzene
a-Pinene
n-Propylbenzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethyl benzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethylbenzene
1-Decene
n-Decane
1,2,3-Trimethylbenzene
m-Diethylbenzene
p-Diethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
15153
11/1/98
11/11/98
2.85
1.86
2.74
1.02
2.30
0.03
0.81
0.33
0.13
1.51
0.18
0.20
0.03
4.95
0.10
0.14
0.83
0.15
0.17
0.13
0.20
0.20
0.04
ND
0.12
0.32
0.49
0.36
0.03
0.03
ND
0.43
0.03
0.01
0.21
0.12
0.80
22.89
0.18
0.16
0.19
ND
0.31
0.15
0.11
0.06
0.13
1.37
0.08
0.07
0.01
0.09
0.24
0.69
0.12
0.28
0.01
0.07
0.06
0.05
0.08
0.26
0.12
0.13
0.10
0.05
0.33
ND
0.10
0.10
0.05
0.05
0.03
0.14
0.01
0.02
0.01
0.01
15197
11/1J/98
12/1(98
4.38
2.90
3.20
1.52
1.97
0.07
2.04
0.56
0.22
3.47
0.45
0.41
0.04
5.61
0.17
0.30
1.13
0.18
0.33
0.21
0.41
0.37
0.13
0.01
0.18
0.52
0.83
0.52
0.06
0.04
ND
0.47
0.06
0.03
0.31
0.15
1.12
1.41
0.29
0.24
0.27
ND
0.42
0.22
0.14
0.09
0.16
1.97
0.11
0.09
ND
0.12
0.32
0.99
0.11
0.40
0.01
0.06
0.06
0.02
0.10
0.31
0.16
0.17
0.15
0.03
0.47
ND
0.08
0.15
0.10
0.08
0.02
0.12
ND
0.01
ND
ND
15235
11/25/98
12/8/98
2.85
2.05
2.84
1.00
2.70
0.05
1.46
0.35
0.14
1.71
0.29
0.28
0.02
4.19
0.10
0.16
0.70
0.14
0.18
0.14
0.20
0.22
0.11
0.01
0.11
0.31
0.52
0.35
0.04
0.02
ND
0.37
0.03
0.02
0.22
0.12
0.82
16.64
0.18
0.13
0.20
ND
0.24
0.16
0.12
0.05
0.09
1.39
0.08
0.08
ND
0.09
0.23
0.66
0.13
0.27
0.01
0.07
0.05
0.04
0.07
0.23
0.12
0.12
0.10
0.05
0.32
ND
0.11
0.13
0.09
0.06
0.04
0.08
ND
0.02
ND
0.001
15249
12/7/98
12/22/96
2.80
2.01
2.95
0.98
3.30
0.03
2.13
0.32
0.13
2.17
0.23
0.22
0.02
5.32
0.12
0.16
0.97
0.15
0.18
0.14
0.20
0.24
0.08
ND
0.13
0.44
0.60
0.44
0.03
0.02
ND
0.55
0.03
0.02
0.33
0.14
0.81
3.14
0.25
0.18
0.24
ND
0.32
0.17
0.13
0.07
0.13
1.64
0.09
0.09
ND
0.10
0.28
0.87
0.11
0.36
0.01
0.06
0.06
0.01
0.09
0.28
0.14
0.15
0.11
0.05
0.32
ND
0.09
0.14
0.18
0.09
0.06
0.17
ND
0.02
ND
0.009
TNMOC (speciated), ppbv
TNMOC (w/ unknowns), ppbC
52.79
324.91
43.84
243.17
47.27
283.85
38.60
243.51
tt • The QC recovery for n-Undecane is outside of QC criteria on 1/11/99
2 of 10
-------
SNMOC OPTION REPORT
SITE CODE: BUVT
Burlington, VT
Reported in ppbv
Sanyle No.: 15284
Sanyling Date: 12/19/98
Analysis Date: 1/11/99
Compound
Ethylene 3.33
Acetylene 2.68
Ethane 3.71
Propylene 0.98
Propane 3.00
Propyne 0.03
Isobutane 1.01
lsobutene/1-Butene 0.29
1.3-Butadiene 0.12
n-Butane 2.00
trans-2-Butene 0.15
cis-2-Butene 0.18
3-Methyl-1-butene ND
Isopentane 3.18
1-Pentene 0.10
2-Methyl-1-butene 0.12
n-Pentane 0.66
Isoprene 0.12
trans-2-Pentene 0.13
cis-2-Pentene 0.11
2-Methyl-2-butene 0.12
2,2-Dimethylbutane 0.17
Cyclopentene 0.10
4-Methyl-1-pentene ND
Cyclopentane 0.11
2,3-Oimethylbutane 0.30
2-Methylpentane 0.46
3-Methylpentane 0.34
2-Methyl-1-pentene 0.02
1-Hexene 0.02
2-Ethyl-1-butene ND
n-Hexane 0.41
trans-2-Hexene 0.02
cis-2-Hexene 0.01
Methylcyclopentane 0.22
2,4-Dimethylpentane 0.11
Benzene 0.79
Cyclohexane 3.78
2-Methylhexane 0.21
2,3-Dimethylpentane 0.16
3-Methylhexane 0.19
1-Heptene ND
2,2,4-Trimethylpentane 0.25
n-Heptane 0.13
Methylcyclohexane 0.12
2,2,3-Trimethylpentane 0.06
2,3.4-Trimethylpentane 0.11
Toluene 1.26
2-Methylheptane 0.08
3-Methylheptane 0.07
1-Octene ND
n-Octane 0.10
Ethylbenzene 0.21
m-Xylene/p-Xylene 0.57
Styrene 0.12
o-Xylene 0.25
1-Nonene 0.01
n-Nonane 0.11
Isopropylbenzene 0.05
a-Pinene 0.11
n-Propylbenzene 0.09
m-Ethyltoluene 0.20
p-Ethyitoluene 0.13
1,3,5-Trimethylbenzene 0.15
o-Ethyltoluene 0.09
b-Pinene 0.04
1,2,4-Trimethylbenzene 0.29
1-Decene ND
n-Decane 0.18
1,2,3-Trimethylbenzene 0.07
m-Diethylbenzene 0.09
p-Diethylbenzene 0.03
1-Undecene 0.04
n-Undeoane 0.16
1-Dodeoene ND
n-Dodecane 0.03
1-Tridecene ND
n-Tridecane 0.01
15310
12/31/98
1/12/99
4.17
3.82
3.26
1.24
2.50
0.05
0.90
0.38
0.17
2.37
0.19
0.23
0.03
2.92
0.10
0.13
0.74
0.15
0.18
0.13
0.19
0.19
0.03
ND
0.15
0.31
0.59
0.43
0.06
ND
ND
0.40
0.03
0.02
0.30
0.15
0.93
0.27
0.27
0.22
0.27
ND
0.41
0.21
0.15
0.09
0.17
1.69
0.11
0.11
ND
0.11
0.32
0.98
0.09
0.41
0.01
0.06
0.07
ND
0.10
0.24
0.13
0.12
0.11
0.01
0.28
ND
0.04
0.09
0.05
0.04
0.01
0.05
ND
ND
ND
0.00
15326
1/12/99
VOID
15354D1
1/24/99
2/2/99
2.94
2.14
3.26
0.93
2.21
0.03
1.64
0.37
0.13
3.73
0.38
0.27
0.03
3.60
0.13
0.13
0.79
0.11
0.19
0.15
0.19
0.19
0.13
0.01
0.13
0.39
0.52
0.35
0.02
0.02
ND
0.30
0.03
0.02
0.22
0.13
0.61
2.62
0.20
0.19
0.20
ND
0.32
0.13
0.10
0.06
0.13
1.18
0.08
0.09
ND
0.09
0.23
0.70
0.08
0.29
0.01
0.06
0.06
0.01
0.08
0.21
0.12
0.11
0.10
0.03
0.32
ND
0.06
0.09
0.07
0.05
0.02
0.09
ND
0.01
ND
0.003
TNMOC (speciated), ppbv
TNMOC (w/ unknowns), ppbC
34.60
197.61
34.76
172.17
34.61
183.21
- The QC recovery for n-Undecane is outside of QC criteria on 1/11/99
3 of 10
-------
SNMOC OPTION REPORT
SITE CODE: BUVT
Burlington, VT
Reported in ppbv
Sanple No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1-Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2.2-Oimethylbutane
Cyclopentene
4-Methyl-1 -pentene
Cyclopentane
2,3-Dimethylbutane
2-Methylpentane
3-Methylpentane
2-Methyt-1 -pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimethylpentane
3-Methylhexane
1-Heptene
2,2,4-Trimethytpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methytheptane
3-Methylheptane
1-Octene
n-Octane
Ethylbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropylbenzene
a-Pinene
n-Propylbenzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethylbenzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethyl benzene
1-Decene
n-Decane
1,2.3-Trimethyl benzene
m-Diethylbenzene
p-Oiethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
1S354R1
1/24/99
2/9/99
2.84
1.68
2.92
0.93
2.14
0.03
1.61
0.37
0.11
3.63
0.29
0.26
0.03
3.59
0.11
0.14
0.77
0.10
0.18
0.13
0.17
0.18
0.19
ND
0.12
0.37
0.49
0.34
0.03
0.02
ND
0.30
0.02
0.02
0.22
0.13
0.57
2.55
0.20
0.18
0.19
ND
0.31
0.14
0.10
0.06
0.12
1.14
0.08
0.07
0.00
0.08
0.21
0.67
0.09
0.28
0.01
0.05
0.06
ND
0.08
0.21
0.12
0.12
0.10
0.03
0.30
ND
0.05
0.09
0.06
0.04
0.03
0.11
0.00
0.01
ND
0.031
15356D2
1/24/99
2/3/99
2.96
2.13
3.25
0.86
1.71
0.03
1.67
0.35
0.11
3.78
0.40
0.26
0.03
2.96
0.13
0.12
0.89
0.13
0.19
0.14
0.19
0.18
0.10
ND
0.14
0.39
0.54
0.35
0.03
0.02
ND
0.31
0.02
0.01
0.26
0.14
0.62
9.48
0.24
0.20
0.21
ND
0.33
0.14
0.11
0.06
0.13
1.21
0.08
0.08
ND
0.09
0.22
0.71
0.12
0.30
0.01
0.06
0.06
0.01
0.08
0.21
0.12
0.12
0.11
0.05
0.33
ND
0.07
0.09
0.08
0.05
0.03
0.13
ND
0.04
ND
0.020
153S6R2
1/24/99
2/9/99
2.86
2.08
2.95
0.85
1.68
0.04
1.62
0.36
0.12
3.58
0.39
0.26
0.02
3.28
0.11
0.12
0.83
0.11
0.18
0.13
0.17
0.17.
0.16
ND
0.11
0.36
0.54
0.34
0.02
0.02
ND
0.31
0.02
0.02
0.24
0.13
0.60
9.06
0.20
0.18
0.20
ND
0.32
0.14
0.10
0.06
0.12
1.16
0.07
0.07
0.01
0.09
0.22
0.68
0.14
0.28
0.01
0.06
0.06
0.02
0.08
0.21
0.12
0.12
0.11
0.05
0.32
ND
0.06
0.09
0.08
0.05
0.03
0.13
0.00
0.04
ND
0.031
1540S
2/5/99
VOID
TNMOC (speciated), ppbv
TNMOC (w/ unknowns), ppbC
33.23
178.07
40.79
228.92
39.52
225.04
# • The QC recovery for n-Undecane is outside of QC criteria on 1/11/99
4 of 10
-------
SNMOC OPTION REPORT
SITE CODE: BUVT
Burlington, VT
Reported in ppbv
Sample No.: 15449 15477 15481 15553
Sampling Date: 2/17/99 2/23/99 3/1/99 3113/99
Analysis Date: 3/4/99 3/11/99 3/11/99 3/24/99
Compound
Ethylene 1.31 1.20 1.87 2.17
Acetylene 0.59 1.00 1.52 1.96
Ethane 1.71 1.13 1.40 2.91
Propylene 0.35 0.36 0.57 0.74
Propane 1.08 0.85 1.02 1.86
Propyne 0.02 0.01 0.02 0.02
Isobutane 0.38 0.25 0.63 0.68
lsobutene/1-Butane 0.11 0.11 0.20 0.28
1,3-Butadiene 0.05 0.05 0.08 0.09
n-Butane 0.77 0.46 1.19 1.20
trans-2-Butene 0.06 0.06 0.14 0.18
cis-2-Butene 0.05 0.06 0.13 0.19
3-Methyl-1-butene 0.10 0.01 ND 0.02
Isopentane 1.26 0.74 1.49 3.10
1-Pentene 0.03 0.03 0.05 0.09
2-Methyl-1-butene 0.05 0.04 0.09 0.17
n-Pentane 0.26 0.20 0.37 0.54
Isoprene 0.02 0.04 0.05 0.10
trans-2-Pentene 0.05 0.05 0.09 0.15
cis-2-Pentene 0.03 0.04 0.06 0.12
2-Methyl-2-butene 0.07 0.05 0.12 0.17
2,2-Dimethylbutane 0.05 - 0.05 0.08 - 0.14
Cyclopentene 0.03 0.02 0.05 0.04
4-Methyl-1-pentene 0.00 ND NO NO
Cyclopentane 0.03 0.03 0.06 0.09
2,3-Dimethylbutane 0.09 0.08 0.19 0.32
2-Methylpentane 0.21 0.15 0.32 0.45
3-Methylpentane 0.08 0.11 0.20 0.31
2-Methy1-1-pentene 0.01 0.01 0.02 0.03
1-Hexene 0.01 0.01 0.01 0.03
2-Ethyl-1-butene ND ND ND ND
n-Hexane 0.14 0.11 0.21 0.28
trans-2-Hexene 0.01 0.01 0.01 0.03
cis-2-Hexene 0.01 0.00 0.18 0.02
Methylcyclopentane 0.08 0.07 0.13 0.21
2,4-Dimethylpentane 0.03 0.04 0.06 0.10
Benzene 0.32 0.30 0.40 0.59
Cyclohexane 0.06 0.11 0.07 0.14
2-Methythexane 0.09 0.07 0.11 0.24
2,3-Dimethylpentane 0.04 0.06 0.08 0.16
3-Mathylhexane 0.08 0.07 0.12 0.21
1-Heptene ND ND 0.01 ND
2.2,4-Trimethylpentane 0.12 0.10 0.17 0.27
n-Heptane 0.05 0.05 0.09 0.12
Methylcyclohexane 0.03 0.04 0.05 0.09
2,2,3-Trimethylpentane 0.03 0.02 0.04 0.06
2,3,4-Trimethylpentane 0.04 0.04 0.07 0.10
Toluene 0.53 0.43 0.72 0.95
2-Methylheptane 0.02 0.03 0.04 0.08
3-Methylheptane 0.02 0.03 0.05 0.07
1-Octene 0.00 0.00 0.00 ND
n-Octane 0.03 0.03 0.04 0.08
Ethylbenzene 0.09 0.08 0.13 0.20
m-Xylene/p-Xylene 0.28 0.25 0.42 0.59
Styrene 0.02 0.02 0.05 0.05
o-Xylene 0.11 0.10 0.17 0.26
1-Nonene 0.01 0.00 0.01 0.01
n-Nonane 0.01 0.02 0.03 0.05
Isopropylbenzene 0.01 0.02 0.02 0.05
a-Pinene 0.04 0.01 0.01 0.02
n-Propylbenzene 0.02 0.02 0.04 0.06
m-Ethyltoluene 0.08 0.06 0.13 0.17
p-Ethyltoluene 0.04 0.03 0.06 0.09
1,3,5-Trimethylbenzene 0.04 0.03 0.07 0.07
o-Ethyltoluene 0.03 0.02 0.05 0.07
b-Pinene 0.01 0.01 0.02 0.01
1,2,4-Trimethylbenzene 0.12 0.06 0.19 0.20
1-Decene ND ND ND ND
n-Decane 0.02 0.01 0.03 0.05
1,2,3-Trimethylbenzene 0.04 0.02 0.05 0.09
m-Diethylbenzene 0.01 0.02 0.05 0.05
p-Diethylbenzene 0.01 0.03 0.02 0.04
1-Undecene 0.02 0.02 0.01 0.03
n-Undecane 0.03 0.03 0.05 0.06
1-Dodecene ND 0.00 0.00 ND
n-Dodecane 0.01 0.00 0.01 0.00
1-Tridecene ND ND ND ND
n-Tridecane 0.008 0.008 0.003 ND
TNMOC (speciated), ppbv 11.64 9.68 16.27 24.19
TNMOC (w/unknowns), ppbC 98.85 55.14 94.14 136.57
# - The QC recovery for n-Undecane is outside of QC criteria on 1 /11 /99 5 of 10
-------
SNMOC OPTION REPORT
SITE CODE: BUVT
Burlington, VT
Reported in ppbv
Sample No.: 15602D1 15604D2 15644 15676
Sampling Date: 3/25/99 3/25/99 4(6/99 4/18/99
Analysis Date: VOID VOID 4/22(99 5/11/99
Compound
Ethylene 3.23 2.61
Acetylene 2.09 1.79
Ethane 3.45 2.92
Propylene 1.01 0.87
Propane 2.53 1.63
Propyne ND 0.04
Isobutane 1.55 2.01
lsobutene/1-Butene 0.39 0.37
1.3-Butadiene 0.12 0.11
n-Butane 2.58 3.55
trans-2-Butene 0.28 0.33
cis-2-Butene 0.28 0.31
3-Methyl-1-butene 0.04 0.04
Isopentane 3.93 3.44
1-Pentene 0.13 0.16
2-Methyl-1-butene 0.24 0.18
n-Pentane 0.85 0.82
Isoprene 0.16 0.11
trans-2-Pentene 0.23 0.26
cis-2-Pentene 0.16 0.16
2-Methyl-2-butene 0.24 0.28
2,2-Dimethylbutane 0.21 0.20
Cyclopentene 0.07 0.04
4-Methyl-1-pentene ND NO
Cyclopentane 0.11 0.11
2,3-Dimethylbutane 0.40 0.42
2-Methylpentane 0.68 0.54
3-Methylpentane 0.37 0.36
2-Methyl-1-pentene 0.04 0.04
1-Hexene 0.03 0.04
2-Ethyl-1-butene ND ND
n-Hexane 0.37 0.30
trans-2-Hexene 0.04 0.03
cis-2-Hexene ND 0.02
Methylcyclopentane 0.26 0.23
2,4-Dimethylpentane 0.14 0.13
Benzene 0.60 0.73
Cyclohexane 4.42 0.26
2-Methylhexane 0.22 0.26
2.3-Dimethylpentane 0.17 0.18
3-Methylhexane 0.24 0.21
1-Heptane ND 0.04
2,2,4-Trimethylpentane 0.33 0.30
n-Heptane 0.16 0.14
Methylcyclohexane 0.13 0.10
2,2,3-Trimethylpentane 0.08 0.07
2,3,4-Trimethylpentane 0.14 0.13
Toluene 2.47 1.15
2-Methylheptane 0.07 0.09
3-Methylheptane 0.08 0.09
1-Octene 0.02 0.02
n-Octane 0.11 0.09
Ethylbenzene 0.26 0.22
m-Xylene/p-Xylene 0.75 0.66
Styrene 0.16 0.09
o-Xylene 0.32 0.28
1-Nonene 0.03 0.02
n-Nonane 0.08 0.05
Isopropylbenzene 0.07 0.07
a-Pinene 0.02 0.02
n-Propylbenzene 0.08 0.08
m-Ethyltoluene 0.23 0.22
p-Ethyltoluene 0.12 0.12
1,3,5-Trimethylbenzene 0.12 0.11
o-Ethyltoluene 0.11 0.09
b-Pinene 0.04 0.03
1,2,4-Trimethylbenzene 0.30 0.29
1-Deoene ND ND
n-Decane 0.09 0.06
1,2,3-Trimethylbenzene 0.09 0.10
m-Diethylbenzene 0.07 0.08
p-Diethylbenzene 0.05 0.08
1-Undecene 0.05 0.05
n-Undecane 0.18 0.13
1-Dodecene ND 0.01
n-Dodecane 0.02 0.02
1-Tridecene ND ND
n-Tridecane 0.006 0.003
TNMOC (speciated), ppbv 38.63 31.20
TNMOC (w/unknowns), ppbC 235.36 188.41
# - The QC recovery for n-Undecane is outside of QC criteria on 1/11/99 6 of 10
-------
SNMOC OPTION REPORT
SITE CODE: BUVT
Burlington, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1-Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethylbutane
Cyclopentene
4-Methyl-1-pentene
Cyclopentane
2,3-Dimethylbutane
2-Methytpentane
3-Methylpentane
2-Methyl-1-pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimethytpentane
3-Methylhexane
1-Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethylbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropylbenzene
a-Pinene
n-Propyl benzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethylbenzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethylbenzene
1-Decene
n-Decane
1,2,3-Trimethyl benzene
m-Diethylbenzene
p-Diethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Oodecane
1-Tridecene
n-Trideoane
15733
4/30/99
5/18/99
4.03
2.45
3.32
1.39
2.14
0.03
1.51
0.48
0.18
2.92
0.32
0.30
0.06
5.32
0.20
0.29
1.08
0.15
0.30
0.20
0.37
0.35
0.09
0.02
0.16
0.59
0.89
0.52
0.05
0.05
ND
0.49
0.07
0.03
0.35
0.20
1.04
0.17
0.32
0.26
0.30
ND
0.51
0.23
0.14
0.12
0.19
1.90
0.11
0.12
0.02
0.11
0.35
1.09
0.15
0.45
0.03
0.07
0.06
0.06
0.11
0.32
0.16
0.17
0.15
0.04
0.48
ND
0.09
0.11
0.08
0.05
0.05
0.13
0.02
0.02
0.01
0.012
15795D1
5/12/99
6/7/99
2.55
1.82
2.73
0.91
1.32
0.03
0.46
0.31
0.11
1.00
0.17
0.19
0.03
3.90
0.12
0.18
0.52
0.13
0.16
0.13
0.16
0.23
0.03
ND
0.10
0.36
0.48
0.29
0.02
0.03
ND
0.26
0.02
0.01
0.19
0.15
0.61
0.17
0.26
0.23
0.20
ND
0.32
0.13
0.10
0.07
0.13
1.08
0.08
0.08
ND
0.09
0.20
0.55
0.06
0.24
0.01
0.06
0.06
0.05
0.06
0.16
0.09
0.09
0.09
0.01
0.21
ND
0.06
0.07
0.04
0.03
0.01
0.07
ND
0.00
ND
ND
15795R1
5/12/99
6/9/99
2.49
1.75
2.74
0.90
1.31
0.02
0.46
0.30
0.12
0.99
0.16
0.18
0.03
0.06
0.12
0.18
0.51
0.17
0.15
0.12
0.16
0.22
0.03
ND
0.09
0.34
0.48
0.28
0.03
0.03
ND
0.25
0.02
0.01
0.20
0.16
0.59
0.17
0.27
0.22
0.20
ND
0.33
0.14
0.10
0.05
0.13
1.10
0.07
0.07
ND
0.09
0.22
0.60
0.09
0.26
0.01
0.06
0.08
0.05
0.09
0.19
0.13
0.11
0.11
0.01
0.27
ND
0.07
0.08
0.06
0.05
0.01
0.08
ND
ND
0.01
ND
15797D2
5/12/99
6/7/99
2.48
1.77
2.72
0.82
1.32
0.03
0.44
0.29
0.11
0.98
0.17
0.19
0.03
1.30
0.11
0.14
0.50
0.13
0.16
0.13
0.15
0.22
0.04
ND
0.10
0.35
0.50
0.30
0.03
0.02
ND
0.25
0.02
0.01
0.19
0.15
0.56
1.72
0.23
0.22
0.17
ND
0.31
0.14
0.10
0.06
0.13
1.08
0.08
0.08
ND
0.10
0.20
0.58
0.10
0.26
0.02
0.06
0.06
0.05
0.07
0.17
0.10
0.11
0.09
0.01
0.24
ND
0.05
0.07
0.05
0.04
0.06
0.05
ND
ND
ND
ND
TNMOC (speciated), ppbv
TNMOC (w/ unknowns), ppbC
40.76
250.62
24.87
140.52
21.28
147.82
23.55
136.63
# - The QC recovery for n-Undecane is outside of QC criteria on 1/11/99
7 of 10
-------
SNMOC OPTION REPORT
SITE CODE: BUVT
Burlington, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1 -Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethylbutane
Cyclopentene
4-Methyl-1 -pentene
Cyclopentane
2,3-Dimethylbutane
2-Methylpentane
3-Methylpentane
2-Methyl-1-pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimethylpentane
3-Methylhexane
1-Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2.3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethylbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropylbenzene
a-Pinene
n-Propylbenzene
m-Ethyltoluene
p-Ethyltoluene
1,3.5-Trimethylbenzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethylbenzene
1-Decene
n-Decane
1,2,3-Trimethylbenzene
m-Diethylbenzene
p-Oiethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
15797R2
5/12/99
6/9/99
2.37
1.72
2.70
0.80
1.31
0.02
0.44
0.28
0.12
0.96
0.16
0.17
0.02
1.28
0.10
0.16
0.51
0.22
0.15
0.13
0.16
0.22
0.03
ND
0.12
0.34
0.49
0.31
0.04
0.02
ND
0.25
0.02
0.02
0.20
0.16
0.53
1.64
0.24
0.22
0.16
ND
0.31
0.13
0.10
0.06
0.12
1.06
0.08
0.07
ND
0.09
0.21
0.59
0.10
0.25
0.01
0.06
0.08
0.06
0.09
0.19
0.12
0.12
0.10
0.01
0.08
ND
0.22
0.07
0.06
0.05
0.03
0.06
ND
0.01
ND
ND
15793
5/24/99
6/8/99
2.08
1.85
2.59
0.79
1.63
0.02
0.57
0.28
0.08
1.31
0.18
0.18
0.02
3.10
0.15
0.13
0.66
0.12
0.16
0.13
0.14
0.26
0.06
ND
0.12
0.44
0.50
0.26
0.02
0.05
ND
0.29
0.02
0.01
0.18
0.12
0.51
0.14
0.26
0.19
0.16
ND
0.28
0.14
0.10
0.06
0.10
1.02
0.08
0.07
ND
0.11
0.18
0.48
0.23
0.21
0.03
0.07
0.11
0.02
0.09
0.17
0.10
0.09
0.08
0.12
0.22
ND
0.06
0.06
0.09
0.04
0.07
0.11
0.00
0.01
ND
0.007
15841
6/5/99
6/17/99
1.98
1.33
2.21
0.70
1.39
ND
0.42
0.27
0.08
0.88
0.14
0.17
0.03
3.90
0.14
0.13
0.53
0.19
0.15
0.13
0.13
0.19
0.02
0.02
0.11
0.19
0.51
0.27
0.03
0.02
ND
0.24
0.02
ND
0.18
0.13
0.47
0.13
0.24
0.19
0.17
ND
0.28
0.12
0.10
0.06
0.12
1.05
0.04
0.14
0.01
0.09
0.19
0.51
0.19
0.22
0.01
0.05
0.06
0.01
0.08
0.18
0.11
0.09
0.09
0.06
0.26
ND
0.06
0.10
0.11
0.08
0.03
0.12
ND
0.01
ND
0.008
1S921
6/17/99
6/29/99
2.54
1.55
2.03
0.88
1.35
ND
0.70
0.33
0.11
1.62
0.27
0.28
0.06
3.98
0.17
0.27
0.78
0.29
0.26
0.18
0.30
0.21
0.03
ND
0.13
0.56
0.66
0.34
0.03
0.04
ND
0.27
0.02
0.02
0.20
0.14
0.55
0.29
0.35
0.24
0.20
0.15
0.31
0.13
0.10
0.06
0.18
1.39
0.08
0.14
0.13
0.10
0.23
0.66
0.25
0.26
0.11
0.07
0.17
0.04
0.08
0.20
0.12
0.12
0.15
0.20
0.28
ND
0.08
0.12
0.08
0.09
0.12
0.20
0.03
0.02
0.01
0.011
TNMOC (speoiated), ppbv
TNMOC (w/ unknowns), ppbC
23.38
142.18
24.38
177.62
22.66
151.49
28.70
201.08
# - The QC recovery for n-Undecane is outside of QC criteria on 1/11/99
8 of 10
-------
SNMOC OPTION REPORT
SITE CODE: BUVT
Burlington, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1-Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethylbutane
Cyclopentene
4-Methyl-1 -pentene
Cyclopentane
2,3-Dimettiylbutane
2-Methylpentane
3-Methylpentane
2-Methyl-1-pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimettiylpentane
3-Methylhexane
1-Heptene
2.2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2.2,3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethylbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropyl benzene
a-Pinene
n-Propylbenzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethylbenzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethylbenzene
1-Decene
n-Decane
1,2,3-Trimethylbenzene
m-Diethyl benzene
p-Oiethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
16024
6/29/99
7/20/99
3.06
1.98
2.96
1.05
1.93
0.06
1.13
0.48
0.14
2.27
0.41
0.42
0.09
9.26
0.22
0.45
1.43
0.37
0.41
0.25
0.49
0.27
0.06
0.02
0.18
0.28
0.83
0.50
0.06
0.04
ND
0.43
0.05
0.03
0.30
0.20
0.78
11.63
0.68
0.42
0.75
NO
0.63
0.62
0.21
0.15
0.21
2.05
0.11
0.09
ND
0.12
0.30
0.80
0.23
0.33
0.02
0.08
0.07
0.05
0.09
0.27
0.14
0.13
0.15
0.12
0.36
ND
0.11
0.08
0.11
0.07
0.05
0.21
0.01
0.06
0.01
0.008
16260
7/17/99
8/10/99
2.88
1.96
3.13
1.07
2.19
ND
3.30
0.53
0.12
2.84
0.49
0.49
0.11
13.24
0.27
0.43
2.88
0.39
0.49
0.31
0.58
0.44
0.12
0.02
0.22
0.35
1.27
0.73
0.07
0.07
ND
0.76
0.08
0.05
0.45
0.23
0.92
9.14
0.57
0.47
0.63
ND
0.56
0.36
0.31
0.15
0.19
3.73
0.15
0.11
0.03
0.18
0.47
1.19
0.40
0.47
0.06
0.22
0.09
0.26
0.14
0.55
0.18
0.21
0.14
0.17
0.47
ND
0.25
0.13
0.10
0.06
0.20
0.30
0.01
0.06
0.01
0.031
16262
7/29/99
8/10/99
3.66
2.44
2.74
1.28
2.06
ND
0.62
0.47
0.16
1.85
0.32
0.34
0.08
3.31
0.26
0.27
1.06
0.38
0.35
0.24
0.39
0.41
0.11
0.02
0.17
0.37
0.94
0.55
0.07
0.04
ND
0.47
0.06
0.03
0.30
0.22
0.82
0.21
0.35
0.35
0.28
ND
0.53
0.20
0.13
0.10
0.19
1.64
0.10
0.11
0.01
0.12
0.29
0.88
0.20
0.35
0.02
0.07
0.06
0.04
0.11
0.27
0.14
0.12
0.12
0.13
0.37
ND
0.12
0.18
0.14
0.06
0.04
0.17
0.01
0.02
0.01
0.012
16277
8/4/99
8/16(99
2.95
1.92
2.26
1.07
1.62
ND
0.46
0.36
0.13
0.94
0.21
0.24
0.05
1.68
0.14
0.17
0.63
0.28
0.24
0.17
0.27
0.26
0.05
0.01
0.13
0.26
0.72
0.36
0.04
0.04
ND
0.27
0.04
0.03
0.20
0.16
0.64
0.28
0.28
0.27
0.22
0.02
0.35
0.12
0.09
0.09
0.15
1.24
0.09
0.10
0.01
0.09
0.24
0.71
0.16
0.29
0.02
0.07
0.07
0.02
0.09
0.21
0.12
0.10
0.10
0.10
0.31
ND
0.09
0.08
0.16
0.07
0.03
0.13
0.02
0.02
0.00
0.015
TNMOC (speciated), ppbv
TNMOC (w/ unknowns), ppbC
54.43
365.63
66.24
512.57
35.34
258.13
25.61
191.36
The QC recovery for n-Undecane is outside of QC criteria on 1/11/99
9of10
-------
SNMOC OPTION REPORT
SITE CODE: BUVT
Burlington, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1-Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethylbutane
Cyclopentene
4-Methyl-1-pentene
Cyclopentane
2,3-Dimethylbutane
2-Methylpentane
3-Methylpentane
2-Methyl-1-pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimethylpentane
3-Methylhexane
1-Heptene
2,2,4-Trimethytpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Ootane
Ethyl benzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropylbenzene
a-Pinene
n-Propylbenzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethylbenzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethylbenzene
1-Decene
n-Decane
1,2,3-Trimethylbenzene
m-Diethylbenzene
p-Diethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
16494
8/16/99
9/3/99
2.21
1.53
1.77
0.99
2.44
ND
1.30
0.42
0.11
3.62
0.48
0.48
0.11
5.27
0.30
0.40
1.61
0.37
0.53
0.31
0.59
0.40
0.06
0.01
0.23
0.39
1.09
0.61
0.07
0.03
ND
0.52
0.08
0.04
0.31
0.21
0.70
0.79
0.34
0.33
0.37
ND
0.45
0.25
0.18
0.08
0.15
1.37
0.07
0.08
0.01
0.10
0.22
0.65
0.15
0.27
0.02
0.06
0.07
0.06
0.07
0.19
0.10
0.08
0.10
0.08
0.26
ND
0.06
0.07
0.07
0.06
0.03
0.13
ND
0.02
ND
0.012
16615
8/28/99
9/14/99
3.43
2.14
2.62
1.35
3.41
ND
1.93
0.56
0.15
3.73
0.59
0.52
0.13
7.03
0.36
0.66
2.65
0.35
0.55
0.34
0.62
0.41
0.07
ND
0.27
0.42
1.33
0.77
0.06
0.05
ND
0.64
0.08
0.04
0.42
0.23
0.93
8.06
0.39
0.35
0.28
ND
0.52
0.21
0.18
0.10
0.18
3.32
0.12
0.13
0.02
0.15
0.54
1.36
0.31
0.50
0.03
0.09
0.08
0.08
0.10
0.28
0.14
0.15
0.13
0.07
0.35
ND
0.14
0.12
0.05
0.05
0.05
0.21
ND
0.02
ND
0.012
16805
9/9/99
10/6/99
2.23
1.58
2.55
0.75
1.30
ND
0.62
0.31
0.10
1.30
0.21
0.23
0.05
2.01
0.16
0.16
0.83
0.23
0.27
0.16
0.23
0.22
0.06
0.01
0.14
0.22
0.73
0.37
0.04
0.03
0.31
ND
0.03
0.01
0.21
0.12
0.60
0.32
0.29
0.19
0.19
0.02
0.29
0.13
0.12
0.06
0.11
1.18
0.06
0.08
0.01
0.10
0.22
0.62
0.19
0.25
0.03
0.06
0.05
0.03
0.07
0.16
0.10
0.09
0.09
ND
ND
0.21
0.06
0.07
0.05
0.04
ND
0.04
0.01
0.02
ND
0.008
16901
9/21/99
10/14/99
2.74
1.68
1.70
0.93
0.91
ND
0.39
0.31
0.12
0.57
0.13
0.15
0.03
1.48
0.10
0.09
0.85
0.16
0.15
0.12
0.14
0.16
0.04
0.03
0.11
0.17
0.56
0.26
0.03
0.03
0.27
ND
0.03
0.02
0.21
0.12
0.56
13.55
0.29
0.21
0.19
0.04
0.24
0.13
0.10
0.05
0.11
1.18
0.08
0.06
0.02
0.08
0.23
0.63
0.30
0.26
0.02
0.06
0.05
0.05
0.09
0.22
0.11
0.10
0.10
0.16
ND
0.23
0.06
0.08
0.06
0.05
0.01
0.05
0.01
0.02
ND
0.009
TNMOC (speciated), ppbv
TNMOC (w/ unknowns), ppbC
36.97
261.73
57.74
402.27
23.95
166.97
34.63
235.44
# - The QC recovery for n-Undecane is outside of QC criteria on 1/11/99
10 of 10
-------
SNMOC OPTION REPORT
SITE CODE: RUVT
Rutland, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1-Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methy1-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethylbutane
Cydopentene
4-Methyl-1-pentene
Cyclopentane
2,3-Dimethylbutane
2-Methylpentane
3-Methylpentane
2-Methyl-1-pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimethylpentane
3-Methylhexane
1-Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethylbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropylbenzene
a-Plnene
n-Propylbenzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethylbenzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethylbenzene
1-Decene
n-Decane
1,2,3-Trimethylbenzene
m-Diethyl benzene
p-Diethyl benzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
14690
9/2/98
9/25/98
1.71
1.24
1.67
0.63
5.01
0.03
0.57
0.23
0.08
1.13
0.16
0.19
0.04
4.78
0.14
0.18
0.77
0.20
0.21
0.15
0.23
0.21
0.09
0.01
0.11
0.38
0.56
0.40
0.04
0.03
NO
0.49
0.05
0.02
0.28
0.12
0.55
0.22
0.21
0.17
0.21
NO
0.38
0.16
0.12
0.07
0.14
1.52
0.07
0.08
0.01
0.12
0.21
0.62
0.23
0.24
0.02
0.10
0.04
0.20
0.07
0.19
0.10
0.11
0.09
0.17
0.26
ND
0.15
0.08
0.04
0.04
0.01
0.09
0.02
0.06
0.01
0.01
14621
9/14/98
10/14/98
2.33
1.60
1.81
0.91
6.43
0.02
1.28
0.28
0.13
1.66
0.28
0.26
0.05
6.66
0.22
0.20
1.09
0.31
0.33
0.21
0.36
0.37
0.09
0.03
0.15
0.60
0.97
0.53
0.08
0.04
ND
0.48
0.09
0.05
0.35
0.15
0.72
18.14
0.27
0.18
0.31
ND
0.45
0.22
0.16
0.11
0.17
1.99
0.09
0.11
0.01
0.12
0.26
0.81
0.30
0.32
0.02
0.08
0.05
0.22
0.08
0.25
0.13
0.12
0.11
0.22
0.33
ND
0.11
0.11
0.06
0.03
0.01
0.08
0.02
0.05
0.01
0.01
14976
9/20/98
10/14/98
1.53
1.18
1.85
0.63
7.83
ND
0.89
0.19
0.07
1.38
0.20
0.22
0.03
5.40
0.16
0.20
0.81
0.28
0.25
0.17
0.26
0.25
0.08
0.02
0.12
0.46
0.65
0.37
0.06
0.04
ND
0.32
0.06
0.04
0.26
0.13
0.53
2.12
0.19
0.15
0.22
ND
0.33
0.16
0.11
0.08
0.13
1.45
0.06
0.08
0.02
0.10
0.23
0.63
0.20
0.26
0.02
0.06
0.05
0.22
0.07
0.24
0.10
0.11
0.09
0.16
0.27
ND
0.11
0.08
0.03
0.04
0.02
0.09
0.01
0.04
0.004
0.01
15060
9/26/98
10/22/98
2.55
1,96 .
2.98
0.94
9.44
0.03
1.13
0.28
0.11
2.00
0.26
0.26
0.05
5,75
0.19
0.24
1.09
0.18
0.33
0.21
0.37
0.33
0.08
0.02
0.15
0.58
0.84
0,53
0.08
0.04
ND
0.50
0.07
0.04
0.38
0.16
0.72
0.20
0.33
0.21
0.33
ND
0.42
0.30
0.25
0.11
0.17
3.40
0.16
0.14
0.02
0.23
0.30
0.98
0.19
0.37
0.04
0.17
0.06
0.23
0.12
0.37
0.18
0.20
0.13
0.12
0.52
ND
0.19
0.12
0.05
0.05
0.02
0.09
0.02
0.07
0.01
0.02
TNMOC (speciated). ppbv
TNMOC (w/ unknowns), ppbC
29.34
179.29
57.23
356.76
35.27
198.67
45.74
257.18
- The QC recovery for n-Undecane was outside of QC criteria on 1/11/99.
1of11
-------
SNMOC OPTION REPORT
SITE CODE: RUVT
Rutland, VT
Reported in ppbv
Sample No.: 15111 15135 15157 15201
Sampling Date: 10/8/98 10/20/98 11/1/98 11/13/98
Analysis Date: 10/22/98 12/6/98 11/11/98 12/1/98
Compound
Ethylene 2.64 1.67 1.16 2.79
Acetylene 1.84 1.47 0.94 2.35
Ethane 1.85 1.96 1.70 2.31
Propylene 0.89 0.64 0.45 0.97
Propane 5.17 4.32 2.01 4.63
Propyne 0.05 0.06 ND 0.02
Isobutane 1.37 0.83 0.81 1.14
lsobutene/1-Butene 0.29 0.21 0.17 0.31
1,3-Butadiene 0.12 0.07 0.04 0.13
n-Butane 2.19 1.49 1.21 1.54
trans-2-Butene 0.26 0.20 0.21 0.30
cis-2-Butene 0.26 0.20 0.18 0.27
3-Methyl-1-butane 0.05 0.01 0.01 0.02
Isopentane 4.66 4.92 3.10 4.61
1-Pentene 0.18 0.17 0.12 0.15
2-Methyl-1-butene 0.25 0.15 0.11 0.21
n-Pentane 0.98 0.56 0.40 0.67
Isoprene 0.15 0.10 0.09 0.13
trans-2-Pentene 0.32 0.21 0.14 0.26
cis-2-Pentene 0.21 0.16 0.12 0.17
2-Methyl-2-butene 0.39 0.25 0.12 0.29
2,2-Dimethylbutane 0.26 0.19 0.15 0.23
Cyclopentene 0.07 0.07 0.02 0.10
4-Methyl-1-pentene 0.02 0.01 ND " 0.02
Cyclopentane 0.14 0.10 0.08 0.14
2,3-Dimethylbutane 0.59 0.29 0.21 0.39
2-Methylpentane 0.78 0.53 0.33 0.65
3-Methylpentane 0.47 0.29 0.23 0.40
2-Methyl-1-pentene 0.08 0.05 0.02 0.06
1-Hexene 0.05 0.05 0.02 0.05
2-Ethyl-1-butene ND ND ND ND
n-Hexane 0.45 0.36 0.20 0.37
trans-2-Hexene 0.12 0.05 0.03 0.07
cis-2-Hexene 0.05 0.03 0.02 0.04
Methylcyclopentane 0.33 0.22 0.14 0.33
2,4-Dimethylpentane 0.16 0.11 . 0.10 0.16
Benzene 0.80 0.52 0.36 0.65
Cyclohexane 1.27 0.14 0.16 0.37
2-Methylhexane 0.28 0.19 0.14 0.26
2,3-Dimethylpentane 0.19 0.15 0.13 0.18
3-Methylhexane 0.27 0.19 0.11 0.25
1-Heptene ND 0.05 0.01 ND
2.2,4-Trimethylpentane 0.50 0.24 0.15 0.37
n-Heptane 0.20 0.14 0.09 0.17
Methylcyclohexane 0.14 0.10 0.08 0.14
2,2,3-Trimethylpentane 0.10 0.05 0.02 0.08
2.3.4-Trimethylpentane 0.21 0.11 0.08 0.15
Toluene 1.93 0.97 0.53 1.45
2-Methylheptane 0.11 0.07 0.05 0.10
3-Methylheptane 0.11 0.07 0.07 0.11
1-Octene 0.02 0.03 0.01 0.01
n-Octane 0.15 0.12 0.08 0.11
Ethylbenzene 0.28 0.16 0.11 0.24
m-Xylene/p-Xylene 0.87 0.49 0.28 0.71
Styrene 0.20 0.13 0.20 0.09
o-Xylene 0.35 0.21 0.12 0.29
1-Nonene 0.03 0.03 0.01 0.02
n-Nonane 0.09 0.08 0.05 0.07
Isopropylbenzene 0.05 0.06 0.06 0.06
a-Pinene 0.09 0.03 0.01 0.02
n-Propylbenzene 0.08 0.07 0.06 0.09
m-Ethyltoluene 0.26 0.17 0.10 0.21
p-Ethyltoluene 0.14 0.10 0.08 0.13
1.3,5-Trimethylbenzene 0.15 0.11 0.07 0.14
o-Ethyltoluene 0.12 0.10 0.05 0.11
b-Pinene 0.12 0.02 0.10 0.01
1,2,4-Trimethylbenzene 0.38 0.27 0.14 0.32
1-Decene ND ND ND ND
n-Decane 0.13 0.08 0.04 0.07
1,2,3-Trimethylbenzene 0.11 0.09 0.04 0.09
m-Diethylbenzene 0.05 0.06 0.04 0.08
p-Diethylbenzene 0.04 0.05 0.03 0.05
1-Undecene 0.01 0.02 0.01 0.005
n-Undecane 0.13 0.06 0.04 0.05
1-Dodecene 0.04 0.01 0.02 ND
n-Dodecane 0.11 0.03 0.01 0.01
1-Trideoene 0.01 ND ND ND
n-Tridecane 0.03 0.004 0.003 ND
TNMOC (speciated), ppbv 37.89 27.59 18.38 33.48
TNMOC (w/unknowns), ppbC 227.07 160.67 106.37 174.61
# - The QC recovery for n-Undecane was outside of QC criteria on 1/11/99. 2 of 11
-------
SNMOC OPTION REPORT
SITE CODE: RUVT
Rutland, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1 -Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2.2-Dimethylbutane
Cyclopentene
4-Methyl-1-pentene
Cyclopentane
2,3-Dimethylbutane
2-Methylpentane
3-Methylpentane
2-Methyl-1-pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2.4-Dimethytpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimethylpentane
3-Methylhexane
1-Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethylpentane
2,3,4-Trimethytpentane
Toluene
2-Methylheptane
3-Methytheptane
1-Octene
n-Octane
Ethylbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropyl benzene
a-Pinene
n-Propylbenzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethyl benzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethylbenzene
1-Decene
n-Decane
1,2,3-Trimethylbenzene
m-Diethylbenzene
p-Diethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Trideoane
15229
11/25/98
12/8/98
2.49
2.14
2.48
O.B9
4.34
0.05
1.41
0.38
0.08
1.87
0.28
0.27
0.04
3.93
0.13
0.16
0.72
0.04
0.23
0.16
0.06
0.23
0.19
0.01
0.12
0.33
0.56
0.37
0.03
0.03
ND
0.33
0.04
0.03
0.25
0.11
0.60
0.76
0.26
0.16
0.22
ND
0.23
0.16
0.12
0.05
0.10
1.20
0.09
0.09
0.01
0.10
0.21
0.58
0.06
0.23
0.01
0.07
0.06
0.002
0.07
0.17
0.10
0.11
0.10
0.01
0.25
ND
0.07
0.07
0.05
0.03
ND
0.04
ND
0.01
ND
0.003
15245
12/7/98
12/22/98
1.19
1.05
2.18
0.53
2.90
0.02
1.10
0.20
0.04
1.60
0.21
0.19
0.03
2.81
0.11
0.11
0.58
0.09
0.15
0.13
0.13
0.17
0.07
ND
0.09
0.25
0.40
0.25
0.03
0.02
ND
0.25
0.02
ND
0.20
0.10
0.37
0.97
0.21
0.13
0.15
0.02
0.14
0.10
0.10
0.03
0.07
0.68
0.06
0.06
0.01
0.09
0.13
0.35
0.12
0.15
0.01
0.05
0.05
0.016
0.06
0.11
0.08
0.07
0.07
0.04
0.17
ND
0.07
0.06
0.04
0.03
0.01
0.04
ND
0.02
ND
0.003
15280
12/19/98
1/11/99
6.60
4.52
4.17
1.85
10.25
0.10
3.17
0.58
0.24
5.54
0.48
0.44
0.11
6.10
0.26
0.34
1.41
0.19
0.38
0.25
0.50
0.40
0.09
0.02
0.21
0.65
1.15
0.71
0.08
0.07
ND
0.70
0.09
0.05
0.50
0.19
1.26
0.42
0.48
0.25
0.42
ND
0.48
0.31
0.19
0.11
0.19
2.29
0.15
0.16
0.02
0.19
0.40
1.26
0.13
0.50
0.02
0.10
0.08
0.097
0.12
0.35
0.18
0.20
0.18
0.01
0.51
ND
0.14
0.14
0.06
0.05
0.01
0.07
ND
0.02
ND
ND
15306
12/31/98
1/12/99
5.45
3.75
3.27
1.55
9.44
0.08
1.42
0.41
0.21
2.99
0.28
0.28
ND
4.21
0.18
0.22
0.92
0.16
0.27
0.19
0.31
0.27
0.04
0.02
0.20
0.45
0.90
0.57
0.05
0.04
ND
0.52
0.06
0.03
0.44
0.18
1.14
0.25
0.36
0.22
0.37
ND
0.43
0.27
0.18
0.10
0.17
1.97
0.14
0.12
0.01
0.14
0.38
1.16
0.11
0.48
0.02
0.08
0.08
0.028
0.11
0.30
0.17
0.17
0.16
0.00
0.38
ND
0.06
0.10
0.05
0.04
0.01
0.04
ND
0.01
ND
0.008
TNMOC (speciated), ppbv
TNMOC (w/ unknowns), ppbC
31.23
189.63
22.12
119.49
63.96
307.64
49.17
237.25
# - The QC recovery for n-Undecane was outside of QC criteria on 1/11/99.
3of11
-------
SNMOC OPTION REPORT
SITE CODE: RUVT
Rutland, VT
Reported in ppbv
Sample No.: 15320 15345D1 15MSR1 15347D2
Sampling Date: 1/12/99 1/24/99 1/24/99 1/24/99
Analysis Date: VOID 2/2/99 2/9/99 2/2/99
Compound
Ethylene 3.55 3.39 3.45
Acetylene 2.46 2.41 2.39
Ethane 2.71 2.60 2.70
Propylene 1.11 1.10 1.05
Propane 10.38 10.06 10.28
Propyne 0.03 0.05 0.04
Isobutane 2.10 2.00 2.06
lsobutene/1-Butene 0.43 0.41 0.44
1,3-Butadiene 0.14 0.14 0.15
n-Butane 4.76 4.62 4.77
trans-2-Butene 0.50 0.48 0.61
cis-2-Butene 0.43 0.40 0.44
3-Methyl-1-butene 0.06 0.05 0.06
Isopentane 4.93 5.00 4.02
1-Pentene 0.22 0.22 0.19
2-Methyl-1-butene 0.28 0.26 0.26
n-Pentane 1.29 1.25 1.24
Isoprene 0.14 0.13 0.15
trans-2-Pentene 0.39 0.36 0.39
cis-2-Pentene 0.24 0.23 0.24
2-Methyl-2-butene 0.44 0.41 0.44
2,2-Dimethylbutane 0.30 0.29 0.29
Cyclopentene 0.14 0.20 0.14
4-Methyl-1-pentene 0.01 0.02 0.01
Cyclopentane 0.20 0.20 0.20
2,3-Dimethylbutane 0.60 0.59 0.61
2-Methylpentane 1.13 1.11 1.06
3-Methylpentane 0.69 0.67 0.69
2-MethyM-pentene 0.08 0.08 0.08
1-Hexene 0.04 0.05 0.05
2-Ethyl-1-butene ND ND ND
n-Hexane 0.60 0.58 0.61
trans-2-Hexene 0.10 0.09 0.10
cis-2-Hexene 0.05 0.05 0.05
Methylcyclopentane 0.48 0.47 0.46
2,4-Dimethylpentane 0.21 0.20 0.20
Benzene 0.78 0.74 0.78
Cyclohexane 1.60 1.55 0.37
2-Methylhexane 0.39 0.39 0.43
2,3-Dimethylpentane 0.27 0.25 0.28
3-Methylhexane 0.40 0.38 0.40
1-Heptene ND NO ND
2,2,4-Trimethylpentane 0.64 0.62 0.63
n-Heptane 0.28 0.28 0.29
Methylcyclohexane 0.18 0.19 0.18
2,2,3-Trimethylpentane 0.14 0.13 0.13
2,3,4-Trimethylpentane 0.25 0.24 0.23
Toluene 2.09 2.02 2.08
2-Methylheptane 0.16 0.15 0.16
3-Methylheptane 0.17 0.16 0.17
1-Octene 0.01 0.01 0.01
n-Octane 0.17 0.17 0.17
Ethylbenzene 0.39 0.37 0.39
m-Xylene/p-Xylene 1.36 1.30 1.36
Styrene 0.17 0.21 0.10
o-Xylene 0.54 0.51 0.54
1-Nonene 0.02 0.02 0.02
n-Nonane 0.11 0.11 0.11
Isopropylbenzene 0.09 0.08 0.09
a-Pinene 0.080 0.087 0.087
n-Propylbenzene 0.15 0.14 0.14
m-Ethyltoluene 0.41 0.38 0.40
p-Ethyltoluene 0.22 0.20 0.21
1,3,5-Trimethylbenzene 0.26 0.24 0.26
o-Ethyltoluene 0.18 0.20 0.21
b-Pinene 0.12 0.13 0.06
1,2,4-Trimethylbenzene 0.65 0.62 0.64
1-Decene ND ND ND
n-Decane 0.19 0.17 0.19
1,2,3-Trimethylbenzene 0.18 0.17 0.15
m-Diethylbenzene 0.08 0.09 0.09
p-Diethylbenzene 0.07 0.07 0.06
1-Undecene 0.01 0.01 0.01
n-Undecane 0.13 0.12 0.12
1-Dodecene ND ND ND
n-Dodecane 0.09 0.09 0.08
1-Tridecene 0.01 0.01 0.00
n-Tridecane 0.019 0.019 0.012
TNMOC (speciated), ppbv 54.28 52.74 51.55
TNMOC (w/unknowns), ppbC 297.94 292.46 277.62
# - The QC recovery for n-Undecane was outside of QC criteria on 1/11/99. 4 of 11
-------
SNMOC OPTION REPORT
SITE CODE: RUVT
Rutland, VT
Reported in ppbv
Sample No.: 15347R2 15409 15445 15479
Sampling Date: 1/24/99 2/5/99 2/17/99 3/1/99
Analysis Date: 2/9/99 2/23(99 3/4/99 3/11/99
Compound
Ethyleno 3.29 1.61 0.87 1.00
Acetylene 2.41 1.44 0.70 0.89
Ethane 2.61 2.54 1.04 1.05
Propylene 1.01 0.58 0.25 0.32
Propane 9.94 3.15 1.93 1.95
Propyne 0.03 ND ND 0.01
Isobutane 1.96 1.11 0.28 0.43
lsobutene/1-Butene 0.41 0.23 0.07 0.10
1,3-Butadiene 0.14 0.05 0.03 0.03
n-Butane 4.55 2.69 0.54 0.68
trans-2-Butene 0.56 0.22 0.04 0.08
cis-2-Butene 0.42 0.22 0.03 0.08
3-Methyl-1-butene 0.06 0.02 ND 0.01
Isopentane 4.00 3.38 1.05 1.10
1-Pentene 0.21 0.10 0.03 0.04
2-Methyl-1-butene 0.24 0.12 0.02 0.05
n-Pentane 1.21 0.66 0.17 0.21
Isoprene 0.14 0.08 0.02 0.04
trans-2-Pentene 0.37 0.18 0.03 0.06
cis-2-Pentene 0.24 0.12 0.02 0.05
2-Methyl-2-butene 0.43 0.17 0.05 0.06
2,2-Dimethylbutane 0.28 0.19 0.03 0.06
Cyclopentene 0.09 0.10 0.02 0.02
4-Methyl-1-pentene ' 0.02 ND ND ND
Cyclopentane 0.19 0.13 0.02 0.04
2,3-Dimethylbutane 0.59 0.28 0.07 0.12
2-Methylpentane 1.04 0.55 0.14 0.18
3-Methylpentane 0.67 0.36 0.08 0.12
2-Methyl-1-pentene 0.07 0.03 0.01 0.01
1-Hexene 0.04 0.03 0.01 0.01
2-Ethyl-1-butene ND ND ND ND
n-Hexane 0.57 0.34 0.10 0.12
trans-2-Hexene 0.08 0.03 0.01 0.01
cis-2-Hexene 0.05 0.02 0.00 0.01
Methylcyclopentane 0.45 0.25 0.06 0.08
2,4-Dimethylpentane 0.20 0.11 0.02 0.04
Benzene 0.81 0.47 0.19 0.23
Cyclohexane 0.37 0.78 0.02 0.05
2-Methylhexane 0.41 0.29 0.06 0.09
2,3-Dimethylpentane 0.27 0.18 0.03 0.06
3-Methylhexane 0.38 0.24 0.05 0.08
1-Heptene ND ND 0.01 ND
2,2,4-Trimethylpentane 0.61 0.28 0.06 0.09
n-Heptane 0.27 0.15 0.03 0.05
Methylcyclonexane 0.18 0.11 0.02 0.04
2,2,3-Trimethytpentane 0.13 0.06 0.01 0.02
2,3,4-Trimethylpentane 0.23 0.11 0.02 0.03
Toluene 2.01 0.91 0.31 0.40
2-Methylheptane 0.16 0.08 0.01 0.03
3-Methylheptane 0.16 0.09 0.01 0.03
1-Octene 0.01 0.01 0.00 0.00
n-Octane 0.16 0.09 0.02 0.04
Ethylbenzene 0.40 0.18 0.05 0.07
m-Xylene/p-Xylene 1.31 0.54 0.15 0.21
Styrene 0.11 0.07 0.03 0.03
o-Xylene 0.53 0.23 0.06 0.09
1-Nonene 0.03 0.01 0.01 0.01
n-Nonane 0.11 0.05 0.01 0.02
Isopropylbenzene 0.09 0.05 0.00 0.02
a-Pinene 0.080 0.009 0.010 0.007
n-Propylbenzene 0.13 0.07 0.01 0.02
m-Ethyltoluene 0.39 0.15 0.04 0.06
p-Ethyltoluene 0.21 0.09 0.02 0.03
1,3,5-Trimethylbenzene 0.25 0.10 0.02 0.04
o-Ethyltoluene 0.20 0.08 0.01 0.03
b-Pinene 0.07 0.01 0.00 0.01
1,2,4-Trimethylbenzene 0.62 0.22 0.05 0.10
1-Decene ND ND ND ND
n-Decane 0.18 0.04 0.01 0.03
1,2,3-Trimethylbenzene 0.16 0.05 0.01 0.03
m-Diethylbenzene 0.07 0.03 0.00 0.01
p-Diethylbenzene 0.06 0.02 0.00 0.01
1-Undecene 0.01 0.00 0.00 0.00
n-Undecane 0.11 0.03 0.01 0.02
1-Dodecene ND ND 0.00 0.00
n-Dodecane 0.08 0.01 0.00 0.01
1-Tridecene 0.01 ND ND ND
n-Tridecane 0.012 0.019 0.006 0.003
TNMOC (speciated), ppbv 49.94 27.00 9.09 11.16
TNMOC (w/ unknowns), ppbC 271.40 140.93 55.57 54.72
- The QC recovery for n-Undecane was outside of QC criteria on 1/11/99. 5 of 11
-------
SNMOC OPTION REPORT
SITE CODE: RUVT
Rutland, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1-Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethylbutane
Cyclopentene
4-Methyl-1-pentene
Cyclopentene
2,3-Dimethylbutane
2-Methylpentane
3-Methylpentane
2-Methyl-1 -pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cydohexane
2-Methylhexane
2,3-Dimethylpentane
3-Methylhexane
1-Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethylbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropyl benzene
a-Pinene
n-Propylbenzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethyl benzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethylbenzene
1-Decene
n-Decane
1,2,3-Trimethylbenzene
m-Diethyl benzene
p-Oiethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1 -Tridecene
n-Tridecane
15SSO
3/13/99
3/24/99
1.23
1.36
2.33
0.51
2.44
ND
1.51
0.36
0.05
1.88
0.28
0.26
0.03
1.46
0.09
0.07
0.41
0.08
0.14
0.12
0.18
0.11
0.01
ND
0.06
0.12
0.29
0.20
0.01
0.01
ND
0.17
0.02
0.01
0.13
0.09
0.38
0.09
0.15
0.12
0.12
ND
0.13
0.08
0.07
ND
0.07
0.48
0.05
0.05
0.01
0.06
0.10
0.26
0.12
0.11
0.01
0.04
0.04
ND
0.03
0.07
0.04
0.04
0.04
0.09
0.09
ND
0.02
0.02
0.01
0.02
ND
0.02
0.01
0.01
ND
ND
15566
3/19/99
4/12/99
1.37
1.11
2.33
0.59
2.34
ND
1.43
0.28
0.04
1.99
0.30
0.30
0.04
3.10
0.16
0.18
0.49
0.10
0.20
0.15
0.14
0.14
0.05
ND
0.10
0.25
0.42
0.23
0.04
0.05
ND
0.22
0.02
0.01
0.19
0.10
0.37
0.16
0.24
0.16
0.14
0.06
0.14
0.09
0.11
ND
0.07
0.50
0.04
0.06
0.05
0.08
0.11
0.29
0.12
0.13
0.03
0.06
0.06
0.223
0.06
0.09
0.07
0.07
0.07
0.03
0.16
ND
0.04
0.04
0.04
0.02
0.01
0.03
0.01
0.01
ND
ND
15628D1
3/25/99
4/16/99
1.12
1.06
2.25
0.40
1.97
ND
1.25
0.24
0.03
1.69
0.28
0.27
0.03
0.84
0.12
0.13
0.43
0.11
0.16
0.14
0.17
0.15
0.02
ND
0.06
0.23
0.34
0.22
0.03
0.03
ND
0.18
0.03
ND
0.17
0.09
0.33
0.13
0.20
0.14
0.13
0.02
0.13
0.08
0.08
ND
0.07
0.48
0.06
0.06
0.02
0.07
0.11
0.28
0.05
0.12
ND
0.05
0.05
ND
0.06
0.07
0.06
0.06
0.06
ND
0.11
ND
0.03
0.04
0.03
0.02
ND
0.02
ND
ND
ND
ND
15628R1
3/25/99
4/21/99
1.14
1.03
2.18
0.46
2.04
ND
1.17
0.31
0.03
1.64
0.24
0.23
ND
1.92
0.11
0.12
0.40
0.09
0.16
0.13
0.15
0.12
0.07
ND
0.05
0.21
0.44
0.20
0.02
0.02
ND
0.17
0.03
ND
0.16
0.10
0.31
0.11
0.20
0.14
0.13
0.03
0.12
0.08
0.09
ND
0.06
0.45
0.06
0.07
0.02
0.07
0.11
0.26
0.06
0.12
0.02
0.05
0.07
ND
0.06
0.08
0.07
0.07
0.06
ND
0.12
ND
0.04
0.05
0.03
0.03
ND
0.03
ND
ND
ND
ND
TNMOC (speciated), ppbv
TNMOC (w/ unknowns), ppbC
19.10
97.64
22.50
123.44
17.44
95.40
18.42
104.88
# - The QC recovery for n-Undecane was outside of QC criteria on 1/11/99.
6 of 11
-------
SNMOC OPTION REPORT
SITE CODE: RUVT
Rutland, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propytene
Propane
Propyne
Isobutane
lsobutene/1-Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2.2-Dimethylbutane
Cyclopentene
4-Methyl-1-pentene
Cyclopentane
2,3-Oimethylbutane
2-Methylpentane
3-Methylpentane
2-Methyl-1-pentene
1-Hexene
2-Ethy1-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimethylpentane
3-Methylhexane
1-Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyctohexane
2,2,3-Trimethylpentane
2,3,4-Trimethytpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethytbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropylbenzene
a-Pinene
n-Propylbenzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethylbenzene
o-Ethyttoluene
b-Pinene
1,2,4-Trimethylbenzene
1-Decene
n-Decane
1,2,3-Trimethylbenzene
m-Diethyl benzene
p-Diethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
15630D2
3/25/99
4/16/99
1.58
1.47
3.78
0.43
2.07
ND
0.69
0.24
0.05
1.32
0.15
0.17
ND
0.72
0.08
0.10
0.48
0.08
0.09
0.10
0.05
0.13
0.02
ND
0.10
0.36
0.30
0.21
ND
ND
ND
0.23
ND
ND
0.17
0.11
0.37
0.23
0.22
0.15
0.15
ND
0.16
0.11
0.09
0.04
0.08
0.70
0.06
0.06
ND
0.09
0.15
0.35
0.15
0.15
0.01
0.10
0.08
0.017
0.07
0.15
0.10
0.08
0.07
0.03
0.19
ND
0.13
0.12
0.11
0.15
0.03
0.20
ND
0.01
ND
0.007
15630R2
3/25/99
4/21/99
1.07
0.96
2.43
0.36
2.07
ND
1.09
0.22
0.03
1.55
0.25
0.23
0.02
0.86
0.10
0.12
0.39
0.11
0.14
0.11
0.12
0.13
0.04
ND
0.08
0.20
0.27
0.20
0.01
0.01
ND
0.17
ND
ND
0.14
0.09
0.30
0.13
0.19
0.13
0.13
0.01
0.11
0.08
0.07
0.02
0.06
0.45
0.06
0.05
ND
0.06
0.10
0.26
0.06
0.12
0.01
0.05
0.06
ND
0.06
0.09
0.07
0.07
0.06
ND
0.13
ND
0.04
0.04
0.04
0.02
0.00
0.03
ND
0.01
ND
ND
15632
4/6/99
4/22/99
2.93
1.95
2.81
0.95
12.55
ND
1.53
0.32
0.10
2.51
0.27
0.28
0.04
4.14
0.15
0.20
0.72
0.13
0.24
0.17
0.25
0.20
0.05
ND
0.11
0.40
0.62
0.41
0.05
0.04
ND
0.43
0.05
0.03
0.27
0.14
0.59
0.21
0.48
0.25
0.50
ND
0.33
0.41
0.17
0.10
0.13
1.83
0.11
0.11
0.02
0.13
0.24
0.70
0.10
0.29
0.02
0.10
0.06
0.059
0.08
0.21
0.12
0.14
0.12
0.04
0.32
ND
0.10
0.08
0.05
0.04
0.01
0.06
ND
0.02
ND
0.005
15678
4/18/99
5/11/99
1.29
4.33
2.17
0.51
5.32
ND
1.29
0.17
0.05
1.42
0.17
0.17
0.03
3.74
0.11
0.10
0.48
0.10
0.16
0.12
0.12
0.20
0.03
ND
0.08
0.25
0.38
0.25
0.03
0.02
ND
0.24
0.02
0.02
0.16
0.10
0.39
6.34
0.20
0.15
0.15
ND
0.20
0.11
0.09
0.05
0.11
0.83
0.07
0.07
0.02
0.10
0.27
0.58
0.39
0.29
0.02
0.13
0.36
0.068
0.59
0.47
0.62
0.32
0.47
0.09
0.82
ND
0.32
0.49
1.23
0.80
0.03
0.79
0.01
0.03
ND
0.020
TNMOC (speciated), ppbv
TNMOC (w/ unknowns), ppbC
20.27
141.01
16.73
93.91
43.37
209.82
41.73
249.27
# - The QC recovery for n-Undecane was outside of QC criteria on 1/11/99.
7 of 11
-------
SNMOC OPTION REPORT
SITE CODE: RUVT
Rutland, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1-Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethylbutane
Cyclopentene
4-Methyl-1 -pentene
Cyclopentane
2,3-Dimethylbutane
2-Methylpentane
3-Methylpentane
2-Methyl-1 -pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimettiylpentane
3-Methylhexane
1-Heptene
2,2.4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethytpentane
2.3.4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethylbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropylbenzene
a-Pinene
n-Propylbenzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethylbenzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethyl benzene
1-Decene
n-Decane
1,2,3-Trimethylbenzene
m-Diethyl benzene
p-Diethy! benzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
15731
4/30/99
5/19/99
2.27
1.62
2.13
0.87
11.74
0.02
1.52
0.31
0.09
3.12
0.30
0.30
0.07
6.1B
0.26
0.37
1.11
0.13
0.39
0.25
0.44
0.33
0.08
0.02
0.18
0.57
0.84
0.51
0.06
0.05
ND
0.50
0.07
0.04
0.33
0.18
0.64
0.23
0.32
0.25
0.25
0.04
0.44
0.20
0.14
0.12
0.17
1.50
0.10
0.11
0.05
0.12
0.23
0.73
0.43
0.30
0.16
0.10
0.08
0.151
0.10
0.23
0.14
0.14
0.11
0.35
0.92
ND
0.14
0.09
0.07
0.06
2.04
2.97
4.96
6.17
7.98
8.177
15822
5/12/99
VOID
15824
5/12/99
VOID
15784
5/24/99
6/7/99
1.55
1.14
1.94
0.65
5.57
ND
0.48
0.20
0.05
0.74
0.21
0.16
0.02
1.11
0.05
0.14
0.79
0.15
0.14
0.13
0.10
0.18
0.03
ND
0.11
0.28
0.38
0.26
0.03
0.02
ND
0.70
0.02
ND
0.25
0.11
0.34
13.76
0.23
0.18
0.16
ND
0.20
0.12
0.11
0.04
0.09
1.00
0.07
0.07
ND
0.10
0.17
0.40
0.24
0.18
0.02
0.10
0.05
0.025
0.06
0.12
0.09
0.08
0.08
0.11
0.17
ND
0.14
0.05
0.04
0.03
ND
0.07
0.01
0.04
ND
0.012
TNMOC (speciated), ppbv
TNMOC (w/ unknowns), ppbC
78.75
672.90
36.44
239.44
# - The QC recovery for n-Undecane was outside of QC criteria on 1/11/99.
8 of 11
-------
SNMOC OPTION REPORT
SITE CODE: RUVT
Rutland, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1 -Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethylbutane
Cyclopentene
4-Methyl-1-pentene
Cyclopentene
2,3-Dimethylbutane
2-Methylpentane
3-Methylpentane
2-Methyl-1-pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcydopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimethytpentane
3-Methythexane
1-Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methytheptane
3-Methylheptane
1-Octene
n-Octane
Ethyl benzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropyl benzene
a-Pinene
n-Propylbenzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethylbenzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethylbenzene
1-Decene
n-Oecane
1,2,3-Trimethylbenzene
m-Diethylbenzene
p-Diethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
15904
6/5/99
6/24/99
2.02
2.13
1.70
0.71
5.20
ND
0.56
0.24
0.07
1.22
0.16
0.19
0.03
1.36
0.20
0.22
0.74
0.25
0.21
0.16
0.20
0.23
0.07
ND
0.12
0.23
0.62
0.36
0.04
0.07
ND
0.33
0.03
0.02
0.26
0.14
0.48
2.64
0.31
0.20
0.21
0.05
0.29
0.17
0.12
O.OB
0.14
1.35
0.09
0.09
0.04
0.14
0.28
0.87
0.41
0.37
0.06
0.08
0.06
0.153
0.11
0.29
0.13
0.15
0.14
0.31
0.39
ND
0.13
0.10
0.06
0.05
0.01
0.07
0.02
0.06
ND
0.011
1S925
6/17/99
VOID
16026
6/29/99
7/20/99
2.66
1.90
2.25
0.97
7.51
ND
1.14
0.40
0.10
2.07
0.33
0.35
0.07
7.96
0.20
0.43
1.50
0.38
0.37
0.24
0.46
0.30
0.12
0.01
0.19
0.32
0.95
0.56
0.07
0.04
ND
0.55
0.07
0.03
0.40
0.19
0.70
73.52
0.82
0.46
1.04
0.05
0.45
0.87
0.35
0.17
0.18
3.67
0.13
0.10
0.02
0.22
0.42
0.98
0.51
0.39
0.04
0.17
0.07
0.524
0.13
0.37
0.17
0.20
0.20
0.33
0.42
ND
0.56
0.15
0.07
0.06
0.01
0.51
0.02
0.26
0.01
0.052
16258
7/17/99
8/10/99
1.59
1.29
2.13
0.69
5.86
ND
0.80
0.27
0.05
1.31
0.18
0.25
0.04
1.45
0.25
0.18
0.83
0.61
0.26
0.18
0.28
0.23
0.15
ND
0.14
0.24
0.79
0.38
0.05
0.04
ND
0.35
0.03
0.03
0.27
0.13
0.55
0.26
0.38
0.24
0.26
ND
0.32
0.17
0.12
0.08
0.13
1.35
0.09
0.07
0.02
0.10
0.23
0.69
0.37
0.26
0.02
0.08
0.07
0.176
0.09
0.21
0.11
0.10
0.11
0.30
0.27
ND
0.12
0.09
0.07
0.05
0.01
0.08
0.02
0.05
0.01
0.024
TNMOC (speciated), ppbv
TNMOC (w/ unknowns), ppbC
30.79
205.53
124.47
853.77
29.06
233.88
# - The QC recovery for n-Undecane was outside of QC criteria on 1/11/99.
9 of 11
-------
SNMOC OPTION REPORT
SITE CODE: RUVT
Rutland, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1-Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-MethyM-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethyl butane
Cyclopentene
4-Methyl-1-pentene
Cyclopentane
2,3-Dimethylbutane
2-Methylpentane
3-Methytpentane
2-Methyl-1-pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dcmethylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimethylpentane
3-Metriylhexane
1-Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethylbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropylbenzene
a-Pinene
n-Propylbenzene
m-Ethyltoluene
p-Ethyttoluene
1,3,5-Trimethylbenzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethylbenzene
1-Decene
n-Decane
1,2,3-Trimethylbenzene
m-Diethyl benzene
p-Diethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
162SO
7/23/99
8/10/99
1.98
1.31
1.81
0.78
7.10
ND
1.02
0.36
0.07
1.86
0.34
0.34
0.07
2.92
0.22
0.27
1.07
1.10
0.38
0.24
0.37
0.29
0.18
0.04
0.17
0.28
0.96
0.51
0.06
0.05
ND
0.46
0.07
0.04
0.33
0.16
0.60
0.21
0.37
0.24
0.23
ND
0.36
0.19
0.12
0.08
0.14
1.58
0.10
0.10
0.02
0.12
0.24
0.68
0.37
0.28
0.02
0.08
0.05
0.343
0.09
0.27
0.12
0.12
0.12
0.33
0.29
ND
0.12
0.10
0.07
0.05
0.01
0.06
0.05
0.05
0.01
0.032
16275
8/4/99
8/16/99
1.62
1.08
1.25
0.67
5.31
ND
0.66
0.27
0.07
1.15
0.24
0.26
0.05
1.86
0.17
0.26
0.67
0.41
0.26
0.18
0.24
0.21
0.08
0.02
0.12
0.23
0.63
0.32
0.04
0.03
ND
0.26
0.03
0.03
0.21
0.11
0.41
3.38
0.28
0.19
0.17
ND
0.27
0.14
0.10
0.06
0.12
1.23
0.08
0.09
0.02
0.12
0.20
0.48
0.22
0.21
0.02
0.08
0.04
0.287
0.07
0.17
0.10
0.08
0.11
0.21
0.21
ND
0.13
0.06
0.05
0.04
0.01
0.08
0.03
0.04
0.01
0.016
16487
8/16/99
9/3/99
1.67
1.17
1.22
0.77
4.44
ND
0.58
0.24
0.06
1.01
0.21
0.23
0.04
1.60
0.15
0.17
0.69
0.37
0.26
0.17
0.24
0.18
0.06
ND
0.15
0.21
0.70
0.36
0.04
0.04
ND
0.35
0.04
0.03
0.22
0.14
0.55
0.11
0.21
0.17
0.30
ND
0.30
0.16
0.14
0.06
0.12
1.26
0.09
0.09
0.02
0.14
0.23
0.65
0.16
0.24
0.02
0.07
0.05
0.286
0.07
0.20
0.09
0.10
0.09
0.15
0.23
ND
0.10
0.07
0.03
0.03
0.01
0.04
0.01
0.04
0.00
0.020
16609
8/28/99
9/14/99
1.95
1.51
1.73
0.86
6.14
ND
0.98
0.27
0.07
1.13
0.22
0.24
0.05
1.81
0.17
0.18
0.75
0.34
0.31
0.21
0.28
0.20
0.07
ND
0.15
0.23
0.71
0.37
0.05
0.03
ND
0.38
0.04
0.03
0.23
0.13
0.70
0.17
0.28
0.22
0.20
0.03
0.25
0.14
0.13
0.06
0.12
1.38
0.06
0.07
0.01
0.12
0.24
0.64
0.18
0.26
0.02
0.07
0.06
0.242
0.07
0.20
0.10
0.11
0.10
0.17
0.24
ND
0.13
0.08
0.04
0.04
ND
0.06
0.01
0.06
0.00
0.015
TNMOC (speciated), ppbv
TNMOC (w/ unknowns), ppbC
35.62
233.80
28.65
187.23
24.54
157.04
28.88
184.81
# - The QC recovery for n-Undecane was outside of QC criteria on 1/11/99.
10 of 11
-------
SNMOC OPTION REPORT
SITE CODE: RUVT
Rutland, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1-Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butane
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethylbutane
Cyclopentene
4-Methyl-1-pentene
Cyclopentane
2,3-Dimethylbutane
2-Methylpentane
3-Methylpentane
2-Methyt-1 -pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimethylpentane
3-Methylhexane
1-Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethylbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropyl benzene
a-Pinene
n-Propylbenzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethyl benzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethylbenzene
1-Decene
n-Oecane
1,2,3-Trimethylbenzene
m-Diethylbenzene
p-Diethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
16807
9/9/99
10/6/99
1.88
1.47
2.23
0.64
5.08
ND
1.16
0.27
0.08
1.21
0.22
0.23
0.05
2.60
0.18
0.18
0.85
0.35
0.28
0.19
0.28
0.20
0.04
ND
0.15
0.24
0.75
0.36
0.05
0.04
0.32
ND
0.04
0.02
0.24
0.14
0.58
0.70
0.25
0.20
0.20
ND
0.33
0.17
0.12
0.09
0.13
1.40
0.07
0.09
0.02
0.13
0.25
0.66
0.27
0.26
0.02
0.07
0.06
0.360
0.08
0.21
0.10
0.10
0.10
0.33
ND
0.22
0.13
0.06
0.04
0.04
0.01
0.06
0.03
0.08
0.01
0.016
16899
9/21/99
VOID
TNMOC (speciated), ppbv
TNMOC (w/ unknowns), ppbC
30.09
196.96
# - The QC recovery for n-Undecane was outside of QC criteria on 1/11/99.
11 of 11
-------
SNMOC OPTION REPORT
SITE CODE: UNVT
Rutland, VT
Reported in ppbv
SanpleNo.: 14680 14815 15052 15109
Sanpling Date: 9/2/98 9/14/98 9/26/98 10/8/98
Analysis Date: VOID 10/19/98 10/22/98 10/22/98
Compound
Ethylene 0.43 0.42 0.75
Acetylene 0.37 0.45 0.55
Ethane 1.33 2.44 1.59
Propylene 0.25 0.18 0.28
Propane 0.83 1.43 1.10
Propyne ND ND ND
Isobutane 0.14 0.26 0.37
lsobutene/1-Butene 0.11 0.09 0.11
1,3-Butadiene ND ND 0.02
n-Butane 0.24 0.45 0.54
trans-2-Butene 0.08 0.06 0.06
cis-2-Butene 0.09 0.09 0.08
3-Methyl-1-butene ND ND ND
Isopentane ND @ 2.55 2.30
1-Pentene 0.05 0.03 0.05
2-Methy1-1-butene 0.02 0.03 0.03
n-Pentane 0.16 0.24 0.29
Isoprene 0.17 0.14 0.10
trans-2-Pentene 0.06 0.04 0.05
cis-2-Pentene 0.07 0.06 0.06
2-Methyl-2-butene 0.01 0.01 0.02
2,2-Dimethylbutane 0.07 0.09 0.10
Cyclopentene 0.03 0.02 0.03
4-Methyl-1-pentene ND ND ND
Cyclopentane 0.04 0.07 0.06
2,3-Dimethylbutane 0.10 0.12 0.19
2-Methylpentane 0.12 0.16 0.25
3-Methylpentane 0.09 0.10 0.18
2-Methy1-1-pentene 0.01 ND 0.01
1-Hexene 0.02 0.01 0.01
2-Ethyl-1-butene ND ND ND
n-Hexane 0.12 0.12 0.23
trans-2-Hexene 0.004 0.03 0.003
cis-2-Hexene ND ND ND
Methylcyclopentane 0.06 0.07 0.09
2,4-Dimethylpentane 0.06 0.06 0.06
Benzene 0.18 0.19 0.25
Cyclohexane 1.28 0.31 3.72
2-Methylhexane 0.07 0.13 0.11
2,3-Dimethylpentane 0.09 0.09 0.09
3-Methylhexane 0.06 0.08 0.10
1-Heptene 0.03 0.01 0.02
2,2,4-Trimethytpentane 0.06 0.07 0.08
n-Heptane 0.05 0.05 0.13
Methylcyclohexane 0.05 0.05 0.11
2,2.3-Trimethylpentane 0.03 0.02 0.03
2,3,4-Trimethylpentane 0.04 0.04 0.05
Toluene 0.19 0.23 0.44
2-Methylheptane 0.03 0.03 0.04
3-Methylheptane 0.03 0.04 0.04
1-Octene 0.02 0.02 0.01
n-Octane 0.05 0.05 0.05
Ethylbenzene 0.05 0.07 0.07
m-Xylene/p-Xylene 0.09 0.10 0.16
Styrene 0.09 0.11 0.11
o-Xylene 0.05 0.07 0.07
1-Nonene 0.02 0.01 0.01
n-Nonane 0.02 0.09 0.05
Isopropylbenzene 0.04 0.09 0.04
a-Pinene 0.04 0.04 0.04
n-Propylbenzene 0.04 0.17 0.04
m-Ethyltoluene 0.05 0.19 0.06
p-Ethyltoluene 0.04 0.03 0.05
1,3,5-Trimethylbenzene 0.03 0.37 0.04
o-Ethyttoluene 0.03 0.03 0.05
b-Pinene 0.04 0.04 0.07
1,2,4-Trimethylbenzene 0.06 0.52 0.09
1-Decene ND ND ND
n-Decane 0.03 0.03 0.05
1,2,3-Trimethylbenzene 0.02 0.12 0.03
m-Diethylbenzene 0.03 0.03 0.02
p-Diethylbenzene 0.02 0.02 0.02
1-Undecene 0.01 0.01 0.01
n-Undecane 0.03 0.03 0.10
1-Dodecene 0.01 0.01 0.01
n-Dodecane 0.01 0.01 0.05
1-Tridecene ND 0.002 0.004
n-Tridecane ND 0.01 0.01
TNMOC (speciated), ppbv 8.29 13.40 16.05
TNMOC (w/unknowns), ppbC 158.52 82.66 101.39
@ - Isopentane can not be quantitated in the 9/14/98 sample due to an analytical interference.
# - The QC recovery for n-Undecane was outside of QC criteria on 1/11/99. 1 of 11
-------
SNMOC OPTION REPORT
SITE CODE: UNVT
Rutland, VT
Reported in ppbv
Sample No.: 15139 15159 15199 15225
Sampling Date: 10/20/98 11/1/98 11/13/98 11/25/98
Analysis Date: 12/6/98 11(11/98 12/1/98 12/8/98
Compound
Ethylene 0.62 0.45 0.59 0.40
Acetylene 0.40 0.47 0.61 0.52
Ethane 1.77 1.56 1.85 1.84
Propylene 0.32 0.22 0.26 0.16
Propane 1.26 1.01 1.36 1.21
Propyne ND ND NO 0.01
Isobutane 0.19 0.24 1.48 0.23
lsobutene/1-Butene 0.13 0.10 0.16 0.10
1,3-Butadiene 0.01 0.01 ND ND
n-Butane 0.40 0.37 1.56 0.41
trans-2-Butene 0.08 0.09 0.14 0.07
cis-2-Butene 0.10 0.10 0.16 0.11
3-Methyl-1-butene 0.05 ND 0.07 ND
Isopentane 2.43 1.61 2.83 1.53
1-Pentene 0.07 0.07 0.09 0.05
2-Methyl-1-butene 0.02 ND 0.08 0.02
n-Pentane 0.21 0.18 0.41 0.17
Isoprene 0.06 0.07 0.08 0.06
trans-2-Pentene 0.06 0.07 0.10 0.05
cis-2-Pentene 0.07 0.08 0.10 0.06
2-Methyl-2-butene 0.01 0.01 0.08 0.01
2,2-Dimethylbutane 0.08 0.09 0.12 0.08
Cyclopentene 0.09 0.02 0.04 0.04
4-Methyl-1-pentene ND ND ND ND
Cyclopentane 0.05 0.05 0.06 0.05
2.3-Dimethylbutane 0.09 0.11 0.15 0.08
2-Methylpentane 0.23 0.08 0.20 0.10
3-Methylpentane 0.09 0.10 0.18 0.09
2-Methyl-1-pentene 0.01 0.01 0.02 0.003
1-Hexene 0.02 0.01 0.01 0.01
2-Ethyl-1-butene ND ND ND ND
n-Hexane 0.12 0.12 0.34 0.09
trans-2-Hexene 0.04 0.05 0.01 0.03
cis-2-Hexene ND ND 0.01 ND
Methylcyclopentane 0.11 0.07 0.15 0.08
2,4-Oimethylpentane 0.08 0.07 0.07 0.06
Benzene 0.24 0.23 0.22 0.17
Cyclohexane 0.11 0.25 57.37 0.10
2-Methylhexane 0.14 0.14 0.09 0.09
2,3-Dimethytpentane 0.08 0.11 0.10 0.09
3-Methylhexane 0.06 0.06 0.10 0.05
1-Heptene 0.03 0.02 ND 0.01
2,2,4-Trimethylpentane 0.06 0.06 0.08 0.05
n-Heptane 0.05 0.06 0.07 0.05
Methylcyclohexane 0.06 0.07 0.07 0.05
2.2,3-Trimethylpentane 0.01 0.03 0.04 0.01
2,3,4-Trimethylpentane 0.05 0.05 0.05 0.04
Toluene 0.19 0.19 0.32 0.16
2-Methylheptane 0.04 0.04 0.04 0.04
3-Methylheptane 0.03 0.04 0.04 0.03
1-Octene 0.02 0.01 0.01 0.01
n-Octane 0.05 0.05 0.05 0.04
Ethylbenzene 0.07 0.06 0.06 0.06
m-Xylene/p-Xylene 0.10 0.11 0.11 0.09
Styrene 0.13 0.07 0.13 0.10
o-Xylene 0.06 0.06 0.06 0.05
1-Nonene 0.02 0.01 0.01 0.01
n-Nonane 0.04 0.04 0.04 0.03
Isopropylbenzene 0.05 0.05 0.05 0.05
a-Pinene 0.00 0.01 0.09 ND
n-Propylbenzene 0.04 0.04 0.05 0.04
m-Ethyltoluene 0.05 0.05 0.06 0.04
p-Ethyltoluene 0.05 0.05 0.07 0.04
1,3,5-Trimethylbenzene 0.04 0.04 0.05 0.04
o-Ethyltoluene 0.04 0.04 0.05 0.04
b-Pinene 0.01 0.01 0.05 0.02
1,2,4-Trimethylbenzene 0.08 0.07 0.09 0.07
1-Decene ND ND ND ND
n-Decane 0.03 0.04 0.05 0.03
1,2,3-Trimethylbenzene 0.04 0.04 0.06 0.04
m-Diethylbenzene 0.05 0.04 0.06 0.03
p-Diethylbenzene 0.03 0.03 0.04 0.02
1-Undeoene 0.01 0.002 ND 0.01
n-Undecane 0.04 0.04 0.06 0.03
1-Dodecene ND 0.001 0.004 ND
n-Dodecane 0.005 0.003 0.02 0.01
1-Tridecene ND ND ND ND
n-Tridecane ND ND 0.003 ND
TNMOC (speciated), ppbv 11.50 9.79 73.32 9.56
TNMOC (w/unknowns), ppbC 141.21 56.75 438.64 51.07
@ - Isopentane can not be quantitated in the 9/14/98 sample due to an analytical interference.
# - The QC recovery for n-Undecane was outside of QC criteria on 1/11/99. 2 of 11
-------
SNMOC OPTION REPORT
SITE CODE: UNVT
Rutland, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethytene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1-Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyt-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethylbutane
Cyclopentene
4-Methyl-1-pentene
Cyclopentane
2,3-Dimethytbutane
2-Methylpentane
3-Methylpentane
2-Methyl-1-pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cts-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimethylpentane
3-Methylhexane
1-Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethylbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropylbenzene
a-Pinene
n-Propyl benzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethyl benzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethylbenzene
1-Decene
n-Decane
1,2,3-Trimethyl benzene
m-Diethylbenzene
p-Diethyl benzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
15247
12/7/98
12722/98
0.49
0.50
2.14
0.19
1.31
ND
0.32
0.10
ND
0.61
0.08
0.11
ND
1.77
0.06
0.03
0.23
0.07
0.06
0.07
ND
0.09
0.06
ND
0.06
0.12
0.13
0.11
0.01
0.01
ND
0.12
ND
ND
0.07
0.07
0.23
0.13
0.10
0.10
0.06
0.01
0.07
0.06
0.06
0.02
0.04
0.19
0.03
0.04
ND
0.05
0.06
0.10
0.07
0.05
0.01
0.04
0.05
ND
0.03
0.04
0.05
0.04
0.03
0.02
0.06
ND
0.03
0.03
0.04
0.02
ND
0.03
ND
0.01
ND
ND
15288
12/19/98
1/11/99
1.22
1.11
2.66
0.38
2.25
ND
0.56
0.15
0.03
0.92
0.09
0.11
ND
2.48
0.06
0.05
0.62
0.10
0.07
0.08
0.05
0.12
0.09
ND
0.09
0.16
0.22
0.18
0.01
0.01
ND
0.25
ND
ND
0.13
0.08
0.35
27.73
0.10
0.10
0.10
ND
0.10
0.09
0.09
0.03
0.06
1.06
0.05
0.06
0.01
0.08
0.13
0.25
0.11
0.12
0.01
0.07
0.05
0.11
0.05
0.18
0.06
0.05
0.06
0.04
0.10
ND
0.11
0.04
0.04
0.02
0.00
0.08 #
ND
0.03
ND
0.009
15308
12/31/98
1/21/99
0.59
0.77
1.82
0.19
2.42
ND
0.28
0.11
ND
0.52
0.04
0.08
ND
0.20
0.05
0.03
0.19
0.06
0.05
0.06
ND
0.10
0.08
ND
0.05
0.09
0.11
0.09
ND
ND
ND
0.12
ND
ND
0.07
0.06
0.24
0.18
0.11
0.09
0.05
ND
0.06
0.05
0.05
ND
0.03
0.16
0.03
0.04
ND
0.04
0.04
0.08
0.04
0.03
ND
0.03
0.04
ND
0.03
0.03
0.03
0.03
0.03
ND
0.05
ND
0.02
0.03
0.02
0.02
ND
0.02
ND
0.00
ND
ND
15322
1/12/99
1/21/99
0.93
0.92
2.64
0.24
2.05
ND
0.41
0.12
0.01
0.79
0.07
0.10
ND
0.38
0.06
0.02
0.29
0.08
0.05
0.06
0.01
0.09
0.04
0.01
0.06
0.12
0.13
0.12
0.02
0.01
ND
0.13
ND
ND
0.09
0.07
0.28
0.50
0.09
0.10
0.07
ND
0.07
0.06
0.06
ND
0.05
0.27
0.04
0.04
ND
0.05
0.06
0.11
0.03
0.05
ND
0.03
0.04
ND
0.04
0.03
0.04
0.04
0.04
ND
0.06
ND
0.02
0.03
0.02
0.01
ND
0.01
ND
ND
ND
0.011
TNMOC (speciated), ppbv
TNMOC (w/ unknowns), ppbC
10.98
56.74
46.08
270.43
9.92
52.03
- Isopentane can not be quantitated in the 9/14/98 sample due to an analytical interference.
- The QC recovery for n-Undecane was outside of QC criteria on 1/11/99. 3 of 11
12.46
59.34
-------
SNMOC OPTION REPORT
SITE CODE: UNVT
Rutland, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1 -Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethylbutane
Cyclopentene
4-Methyl-1 -pentene
Cyclopentane
2,3-Dimethylbutane
2-Methylpentane
3-Methylpentane
2-Methyl-1-pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimethylpentane
3-Methythexane
1-Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethylpentane
2,3.4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethylbenzene
m-Xylene/p-Xylene
Styrene
o-Xytene
1-Nonene
n-Nonane
Isopropylbenzene
a-Pinene
n-Propylbenzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethylbenzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethylbenzene
1-Deoene
n-Decane
1,2,3-Trimethylbenzene
m-Diethylbenzene
p-Diethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
15358D1
1/24/99
2/3/99
0.58
0.55
1.91
0.18
1.27
ND
0.34
0.10
ND
0.61
0.07
0.11
ND
0.92
0.07
0.01
0.21
0.06
0.06
0.07
0.01
0.09
0.07
ND
0.06
0.14
0.14
0.12
0.01
0.01
ND
0.11
ND
ND
0.09
0.08
0.21
2.79
0.11
0.10
0.07
0.01
0.08
0.06
0.06
ND
0.05
0.24
0.04
0.04
0.01
0.05
0.06
0.12
0.09
0.06
0.01
0.04
0.05
0.01
0.04
0.05
0.05
0.04
0.04
0.03
0.07
ND
0.04
0.04
0.04
0.03
ND
0.04
ND
0.01
ND
0.016
15358R1
1/24/99
2/9/99
0.55
0.53
1.70
0.20
1.22
ND
0.31
0.11
0.01
0.58
0.05
0.10
ND
0.96
0.06
0.01
0.21
0.06
0.06
0.07
ND
0.08
0.09
ND
0.04
0.13
0.14
0.11
0.01
0.01
ND
0.12
ND
ND
0.08
0.07
0.20
2.69
0.11
0.09
0.07
0.01
0.07
0.05
0.05
ND
0.04
0.23
0.03
0.04
0.01
0.05
0.06
0.12
0.09
0.06
0.00
0.04
0.05
0.00
0.04
0.05
0.05
0.04
0.05
0.02
0.08
ND
0.04
0.04
0.05
0.03
0.00
0.04
ND
0.01
ND
0.029
15360D2
1/24/99
2/3/99
0.55
0.59
1.97
0.18
1.20
ND
0.30
0.09
0.01
0.59
0.06
0.11
ND
0.31
0.05
0.20
ND
0.07
0.05
0.07
ND
0.08
0.05
ND
0.06
0.13
0.11
0.12
0.01
0.00
ND
0.12
ND
ND
ND
0.07
0.20
0.80
0.09
0.10
0.06
0.01
0.07
0.06
0.07
0.05
0.04
0.24
0.04
0.04
ND
0.05
0.06
0.12
0.08
0.06
ND
0.05
0.05
0.01
0.04
0.05
0.05
0.04
0.04
0.03
0.07
ND
0.04
0.03
0.04
0.03
0.00
0.03
ND
0.00
ND
ND
15360R2
1/24/99
2/11/99
1.11
0.86
2.04
0.35
1.68
ND
0.47
0.14
0.07
1.26
0.09
0.12
ND
0.75
0.07
0.04
0.30
0.08
0.08
0.08
0.04
0.09
0.13
ND
0.07
0.17
0.22
0.20
0.01
0.01
ND
0.25
ND
ND
0.12
0.08
0.26
0.69
0.12
0.11
0.09
ND
0.11
0.06
0.06
0.02
0.06
0.42
0.04
0.04
0.01
0.07
0.09
0.20
0.12
0.10
0.01
0.05
0.06
0.08
0.06
0.08
0.07
0.06
0.06
0.04
0.12
ND
0.05
0.04
0.05
0.03
ND
0.06
ND
0.01
ND
0.026
TNMOC (speciated), ppbv
TNMOC (w/ unknowns), ppbC
12.93
73.34
12.40
73.15
10.02
55.72
15.25
79.97
: • Isopentane can not be quantitated in the 9/14/98 sample due to an analytical interference.
- The QC recovery for n-Undecane was outside of QC criteria on 1/11/99. 4 of 11
-------
SNMOC OPTION REPORT
SITE CODE: UNVT
Rutland, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysts Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1-Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethylbutane
Cyclopentene
4-Methyl-1-pentene
Cyclopentane
2,3-Dimethylbutane
2-Methylpentane
3-Methylpentane
2-Methyl-1-pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methylhexane
2.3-Dimethylpentane
3-Methylhexane
1 -Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethylbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropylbenzene
a-Pinene
n-Propyl benzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trtmethylbenzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethylbenzene
1-Decene
n-Decane
1,2,3-Trimethylbenzene
m-Diethylbenzene
p-Diethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
15417
2/5/99
2/23/99
0.44
0.59
2.11
0.18
1.36
ND
0.28
0.10
ND
0.56
0.06
0.08
0.08
0.71
0.05
ND
0.21
0.05
0.05
0.06
0.02
0.08
0.10
0.03
0.05
0.10
0.10
0.10
ND
ND
ND
0.11
0.04
ND
0.07
0.06
0.26
0.09
0.14
0.09
0.06
0.11
0.06
0.05
0.05
0.02
0.04
0.18
0.03
0.04
0.01
0.05
0.08
0.13
0.12
0.07
0.02
0.04
0.05
0.04
0.04
0.04
0.05
0.08
0.04
0.01
0.15
ND
0.03
0.03
0.03
0.01
0.02
0.02
0.006
0.00
0.01
0.003
15447
2/17/99
3/4/99
0.24
0.29
0.82
0.05
0.52
ND
0.11
0.02
ND
0.20
ND
0.00
ND
0.34
ND
ND
0.07
ND
ND
ND
0.01
0.01
0.03
ND
0.01
0.03
0.05
0.02
ND
ND
ND
0.02
ND
ND
0.02
0.01
0.08
0.05
0.04
0.01
0.01
ND
0.01
0.01
0.00
0.01
0.01
0.08
0.00
ND
ND
0.00
0.01
0.02
0.04
0.01
ND
0.00
0.00
ND
0.00
0.01
0.00
ND
ND
0.02
0.01
ND
0.00
ND
ND
ND
ND
0.00
ND
0.00
ND
0.007
15485
3/1/99
3/11/99
0.33
0.37
0.86
0.10
0.69
ND
0.51
0.05
0.01
0.28
0.02
0.03
ND
1.20
0.02
0.09
0.15
0.03
0.02
0.03
0.01
0.03
0.01
ND
0.03
0.05
0.09
0.06
0.00
0.00
ND
0.10
0.01
ND
0.04
0.03
0.11
8.20
0.04
0.03
0.04
ND
0.03
0.03
0.03
ND
0.02
0.15
0.01
0.01
0.00
0.02
0.03
0.05
0.05
0.03
0.00
0.02
0.02
0.01
0.01
0.02
0.02
0.02
0.02
0.01
0.03
ND
0.03
0.01
0.01
0.01
ND
0.02
ND
0.01
ND
0.002
15544
3/13/99
3/24/99
0.51
0.76
2.28
0.22
1.47
ND
0.33
0.12
ND
0.52
0.08
0.11
ND
2.07
0.07
0.02
0.23
0.06
0.06
0.07
ND
0.09
0.01
ND
0.05
0.10
0.16
0.12
ND
ND
ND
0.11
ND
ND
0.07
0.06
0.25
1.68
0.11
0.09
0.08
ND
0.05
0.07
0.05
ND
0.04
0.19
0.03
0.04
ND
0.04
0.05
0.08
0.06
0.04
0.01
0.04
0.03
0.01
0.03
0.03
0.03
0.02
0.03
0.02
0.05
ND
0.02
0.02
0.02
0.01
ND
0.02
0.023
0.01
ND
0.005
TNMOC (speciated), ppbv
TNMOC (w/ unknowns), ppbC
10.24
64.92
3.31
32.31
@ • Isopentane can not be quantitated in the 9/14/98 sample due to an analytical interference.
# • The QC recovery for n-Undecane was outside of QC criteria on 1/11/99. 5 of 11
14.41
81.94
13.17
69.71
-------
SNMOC OPTION REPORT
SITE CODE: UNVT
Rutland, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1-Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethylbutane
Cyclopentene
4-Methyl-1 -pentene
Cyclopentane
2,3-Dimethylbutane
2-Methylpentane
3-Methylpentane
2-Methyl-1 -pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimethylpentane
3-Methylhexane
1-Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethylbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropylbenzene
a-Pinene
n-Propylbenzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethylbenzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethylbenzene
1-Decene
n-Decane
1,2,3-Trimethylbenzene
m-Diethyl benzene
p-Diethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
15568
3/19/99
4/12/99
0.34
0.57
2.14
0.22
1.19
ND
0.22
0.12
ND
0.38
0.11
0.11
ND
0.55
0.10
0.03
0.17
0.07
0.07
0.08
ND
0.09
ND
ND
0.04
0.10
0.10
0.09
ND
ND
ND
0.10
0.05
ND
0.07
0.08
0.19
0.13
0.12
0.09
0.06
ND
0.06
0.05
0.06
0.02
0.04
0.14
0.03
0.05
0.03
0.06
0.06
0.08
0.08
0.03
0.02
0.03
0.05
ND
0.04
0.03
0.05
0.04
0.04
0.01
0.07
ND
0.03
0.03
0.03
0.02
0.01
0.02
0.007
ND
ND
ND
15580D1
3/25/99
4/22/99
0.42
0.53
1.91
0.19
0.98
ND
0.21
0.11
ND
0.34
0.12
0.11
ND
0.80
0.07
0.03
0.14
0.08
0.06
0.07
ND
0.10
0.02
ND
0.04
0.10
0.11
0.10
0.01
0.02
ND
0.09
ND
ND
0.09
0.06
0.18
0.77
0.16
0.10
0.06
0.01
0.05
0.05
0.05
ND
0.04
0.13
0.04
0.03
0.02
0.06
0.05
0.07
0.06
0.05
0.02
0.03
0.05
ND
0.05
0.04
0.04
0.04
0.05
ND
0.07
ND
0.02
0.03
0.03
0.02
ND
0.03
ND
0.01
ND
0.012
15580R1
3/25/99
4/23/99
0.39
0.46
1.91
0.24
0.94
ND
0.21
0.11
ND
0.35
0.09
0.12
ND
0.85
0.08
0.05
0.13
0.07
0.06
0.07
0.02
0.09
0.03
ND
0.04
0.11
0.12
0.11
ND
ND
ND
0.11
ND
ND
0.09
0.06
0.19
0.79
0.16
0.10
0.06
0.02
0.06
0.06
0.04
ND
0.04
0.15
0.04
0.05
0.02
0.06
0.05
0.09
0.06
0.05
0.01
0.04
0.05
ND
0.04
0.03
0.04
0.03
0.04
ND
0.05
ND
0.03
0.03
0.02
0.01
ND
0.03
ND
0.01
ND
ND
15582D2
3/25/99
4/16/99
0.39
0.55
2.04
0.18
0.93
ND
0.20
0.10
0.01
0.35
0.11
0.10
ND
0.16
0.05
0.04
0.14
0.07
0.07
0.08
ND
0.10
0.02
ND
0.05
0.11
0.10
0.10
ND
ND
ND
0.10
ND
ND
0.08
0.07
0.19
0.53
0.11
0.10
0.06
ND
0.04
0.05
0.05
ND
0.04
0.13
0.04
0.05
ND
0.05
0.04
0.08
0.09
0.04
ND
0.04
0.05
ND
0.04
0.03
0.05
0.04
0.05
0.02
0.07
ND
0.03
0.03
0.03
0.02
0.01
0.02
ND
0.01
ND
0.010
TNMOC (speciated), ppbv
TNMOC (w/ unknowns), ppbC
9.12
56.47
9.43
63.02
@ - Isopentane can not be quantitated in the 9/14/98 sample due to an analytical interference.
# - The QC recovery for n-Undecane was outside of QC criteria on 1/11/99. 6 of 11
9.43
64.01
8.50
52.44
-------
SNMOC OPTION REPORT
SITE CODE: UNVT
Rutland, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1-Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethylbutane
Cyclopentene
4-Methyl-1-pentene
Cyclopentane
2,3-Dimethylbutane
2-Methylpentane
3-Methylpentane
2-Methyl-1-pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methytcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimethylpentane
3-Methylhexane
1-Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethyl benzene
m-Xytene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropyl benzene
a-Pinene
n-Propylbenzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethylbenzene
o-Ethyrtoluene
b-Pinene
1,2,4-Trimethylbenzene
1-Decene
n-Decane
1,2,3-Trimethylbenzene
m-Diethylbenzene
p-Diethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
15582R2
3/25/99
4/22/99
0.35
0.53
1.97
0.17
0.91
ND
0.19
0.10
ND
0.37
0.06
0.12
ND
0.19
0.07
0.03
0.14
0.07
0.07
0.07
ND
0.08
0.02
ND
0.03
0.10
0.09
0.09
ND
ND
ND
0.09
ND
ND
0.09
0.07
0.17
0.48
0.15
0.10
0.06
ND
0.05
0.05
0.05
ND
0.04
0.13
0.04
0.04
ND
0.05
0.04
0.08
0.09
0.04
ND
0.04
0.05
ND
0.04
0.03
0.05
0.04
0.04
0.02
0.06
ND
0.02
0.02
0.04
0.02
ND
0.02
ND
0.01
ND
0.007
15642
4/6/99
4/22/99
0.57
0.80
1.99
0.22
1.12
ND
0.25
0.11
ND
0.41
0.08
0.12
ND
2.3B
0.06
ND
0.19
0.07
0.05
0.08
0.01
0.10
0.03
ND
0.04
0.11
0.10
0.10
ND
ND
ND
0.10
ND
ND
0.07
0.07
0.22
0.10
0.11
0.10
0.06
0.01
0.07
0.06
0.04
ND
0.04
0.21
0.04
0.05
0.01
0.06
0.07
0.10
0.07
0.06
0.01
0.04
0.05
ND
0.05
0.04
0.05
0.04
0.04
0.02
0.07
ND
0.03
0.03
0.04
0.02
ND
0.03
ND
ND
ND
ND
15666
4/12/99
5/10/99
0.36
0.52
1.99
0.19
0.97
ND
0.19
0.10
ND
0.34
0.06
0.10
ND
0.60
0.06
ND
0.14
0.07
0.06
0.07
ND
0.09
0.02
ND
0.05
0.10
0.09
0.10
0.01
0.01
ND
0.08
ND
ND
0.07
0.07
0.20
0.08
0.11
0.11
0.06
0.01
0.06
0.05
0.06
ND
0.05
0.16
0.04
0.04
0.02
0.05
0.07
0.08
0.08
0.05
0.01
0.04
0.05
ND
0.04
0.04
0.05
0.03
0.04
0.02
0.06
ND
0.03
0.03
0.04
0.02
ND
0.03
0.003
0.01
ND
ND
15735
4/30/99
5/18/99
0.37
0.33
1.48
0.21
0.63
ND
0.15
0.11
ND
0.21
0.08
0.10
ND
0.94
0.08
ND
0.16
0.07
0.06
0.07
ND
0.08
0.03
ND
0.05
0.10
0.11
0.08
0.03
ND
ND
0.10
ND
ND
0.08
0.07
0.13
1.09
0.13
0.10
0.06
0.03
0.06
0.06
0.04
ND
0.04
0.16
0.04
0.04
0.04
0.05
0.06
0.08
0.07
0.05
0.02
0.03
0.05
ND
0.04
0.03
0.04
0.03
0.03
0.01
0.07
ND
0.02
0.03
0.03
0.02
0.01
0.02
ND
0.01
ND
ND
TNMOC (speciated), ppbv
TNMOC (w/ unknowns), ppbC
8.25
54.14
11.28
60.06
- Isopentane can not be quantitated in the 9/14/98 sample due to an analytical interference.
- The QC recovery for n-Undecane was outside of QC criteria on 1/11/99. 7 of 11
6.42
54.35
8.59
62.96
-------
SNMOC OPTION REPORT
SITE CODE: UNVT
Rutland, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1-Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethylbutane
Cyclopentene
4-Methyl-1-pentene
Cyclopentane
2,3-Dimethylbutane
2-Methylpentane
3-Methylpentane
2-Methyl-1-pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimethylpentane
3-Methylhexane
1-Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methyl heptane
1-Octene
n-Octane
Ethylbenzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropylbenzene
a-Pinene
n-Propylbenzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethylbenzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethylbenzene
1-Decene
n-Decane
1,2,3-Trimethyl benzene
m-Diethylbenzene
p-Diethyl benzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
15799D1
5/12/99
6f7/99
0.36
0.47
1.62
0.23
0.70
ND
0.15
0.11
ND
0.24
0.12
0.11
NO
0.60
0.08
0.02
0.14
0.09
0.06
0.08
0.01
0.13
0.02
ND
0.04
0.10
0.15
0.09
0.01
0.01
ND
0.09
ND
ND
0.07
0.07
0.13
0.18
0.15
0.11
0.05
0.02
0.06
0.05
0.06
ND
0.04
0.15
0.03
0.04
ND
0.05
0.06
0.09
0.05
0.05
0.01
0.04
ND
ND
0.04
0.04
0.04
0.03
0.04
ND
0.06
ND
0.03
0.03
0.03
0.02
0.01
0.03
ND
ND
ND
ND
15799R1
5/12799
6/9/99
0.38
0.48
1.68
0.23
0.75
ND
0.17
0.10
ND
0.26
0.08
0.11
ND
0.76
0.08
ND
0.11
0.16
0.15
0.08
0.02
0.12
0.04
ND
0.05
0.10
0.14
0.10
0.01
0.02
ND
0.11
ND
ND
0.10
0.08
0.14
0.18
0.17
0.11
0.06
0.02
0.06
0.05
0.07
ND
0.04
0.18
0.05
0.04
ND
0.05
0.08
0.10
0.08
0.06
0.01
0.04
0.06
0.01
0.06
0.05
0.06
0.05
0.06
0.01
0.09
ND
0.04
0.04
0.05
0.03
0.01
0.04
ND
ND
ND
ND
15801D2
5/12/99
6/7/99
0.36
0.45
1.65
0.20
0.64
ND
0.22
0.10
ND
0.23
0.11
0.10
ND
0.26
0.08
0.02
0.21
0.08
0.06
0.08
0.01
0.11
0.02
ND
0.06
0.11
0.10
0.09
0.01
0.02
ND
0.12
ND
ND
0.07
0.06
0.13
0.22
0.15
0.11
0.06
0.02
0.05
0.06
0.05
ND
0.04
0.16
0.04
0.04
ND
0.05
0.06
0.08
0.04
0.04
0.01
0.03
0.05
ND
0.03
0.04
0.04
0.03
0.04
ND
0.06
ND
0.03
0.03
0.03
0.02
ND
0.02
ND
ND
ND
ND
15801R2
5/12/99
6/9/99
0.37 .
0.48
1.68
0.21
0.66
ND
0.22
ND
ND
0.24
0.09
0.12
ND
0.28
0.08
0.08
0.25
0.11
0.07
0.08
0.02
0.12
0.02
ND
0.06
0.11
0.09
0.10
0.01
0.02
ND
0.13
ND
ND
0.08
0.07
0.14
0.23
0.17
0.12
0.06
0.02
0.06
0.06
0.07
ND
0.04
0.16
0.05
0.04
ND
0.06
0.07
0.10
0.06
0.07
0.02
0.04
0.06
ND
0.06
0.05
0.06
0.05
0.05
ND
0.08
ND
0.04
0.04
0.05
0.03
0.01
0.04
ND
ND
ND
ND
TNMOC (speciated), ppbv
TNMOC (w/ unknowns), ppbC
7.79
58.59
8.70
67.00
: - Isopentane can not be quantitated in the 9/14/98 sample due to an analytical interference.
- The QC recovery for n-Undecane was outside of QC criteria on 1/11/99. 8 of 11
7.47
50.30
8.10
56.04
-------
SNMOC OPTION REPORT
SITE CODE: UNVT
Rutland, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1 -Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethylbutane
Cyclopentene
4-Methyl-1-pentene
Cyclopentane
2,3-Dimethylbutane
2-Methylpentane
3-Methylpentane
2-Methy1-1 -pentene
1-Hexene
2-Ethyl-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Metnylhexane
2,3-Dimethylpentane
3-Methylhexane
1-Heptene
2,2,4-TrimethyIpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethyl benzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropylbenzene
a-Pinene
n-Propylbenzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethylbenzene
o-Ethyltoluene
b-Pinene
1,2.4-Trimethylbenzene
1-Decene
n-Decane
1,2,3-Trimethylbenzene
m-Diethylbenzene
p-Oiethylbenzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
15791
5/24/99
6/7/99
0.33
0.38
1.59
0.20
0.82
ND
0.13
0.11
ND
0.22
0.08
0.11
ND
0.17
0.06
ND
0.16
0.08
0.06
ND
0.07
0.11
0.05
ND
0.05
0.10
0.11
0.09
ND
ND
ND
0.08
ND
ND
0.08
0.07
0.12
0.17
0.15
0.11
0.04
0.02
0.06
0.06
0.05
ND
0.04
0.14
0.04
0.04
ND
0.05
0.05
0.07
0.12
0.04
ND
0.03
0.04
ND
0.04
0.03
0.04
0.04
0.04
0.07
0.06
ND
0.03
0.03
0.03
0.02
0.01
0.04
ND
0.01
ND
ND
15830
6/5/99
6/17/99
0.30
0.37
1.31
0.18
0.57
ND
0.13
0.10
ND
0.22
0.07
0.10
0.02
0.17
0.05
ND
0.13
0.25
0.06
0.07
0.02
0.11
0.03
0.01
0.05
0.10
0.18
0.09
ND
ND
ND
0.10
ND
ND
0.08
0.07
0.11
0.62
0.15
0.10
0.05
0.01
0.06
0.05
0.05
ND
0.04
0.15
0.04
0.04
0.01
0.03
0.05
0.07
0.13
0.05
ND
0.03
0.06
0.06
0.04
0.04
0.04
0.03
0.04
0.08
0.05
ND
0.03
0.02
0.03
0.02
ND
0.03
ND
0.01
ND
0.009
15923
6/17/99
6/29/99
0.30
0.23
1.13
0.21
0.61
ND
0.12
0.10
ND
0.22
0.11
0.12
ND
0.20
0.08
ND
0.16
0.35
0.06
0.08
0.01
0.10
0.03
ND
0.06
0.35
0.16
0.09
ND
ND
ND
0.51
ND
ND
0.05
0.06
0.10
0.28
0.44
0.11
0.06
0.15
0.05
0.05
0.05
ND
0.28
1.95
0.04
0.40
0.12
0.05
0.06
0.10
0.16
0.06
0.10
0.04
0.18
0.06
0.04
0.05
0.05
0.04
0.71
0.11
0.06
ND
0.03
0.03
0.03
0.34
0.06
0.07
0.025
0.01
0.00
0.012
16028
6/29/99
7/20/99
0.40
0.43
1.84
0.21
1.08
ND
0.19
0.12
ND
0.31
0.06
0.13
ND
0.38
0.11
0.00
0.23
0.71
0.06
0.08
0.03
0.13
0.04
ND
0.06
0.13
0.18
0.12
0.01
0.01
ND
0.14
ND
ND
0.09
0.10
0.16
4.11
0.31
0.23
0.32
0.03
0.23
0.24
0.12
0.07
0.12
1.17
0.13
0.12
0.04
0.16
0.26
0.93
0.13
0.41
0.03
0.08
0.06
0.18
0.09
0.25
0.13
0.14
0.15
0.04
0.32
ND
0.14
0.11
0.06
0.05
0.01
0.18
ND
0.03
ND
ND
TNMOC (speciated), ppbv
TNMOC (w/ unknowns), ppbC
7.21
56.62
7.38
139.67
12.06
107.16
18.72
151.96
@ - Isopentane can not be quantitated in the 9/14/98 sample due to an analytical interference.
# - The QC recovery for n-Undecane was outside of QC criteria on 1/11/99. 9 of 11
-------
SNMOC OPTION REPORT
SITE CODE: UNVT
Rutland, VT
Reported in ppbv
Sample No.:
Sampling Date:
Analysis Date:
Compound
Ethylene
Acetylene
Ethane
Propylene
Propane
Propyne
Isobutane
lsobutene/1 -Butene
1,3-Butadiene
n-Butane
trans-2-Butene
cis-2-Butene
3-Methyl-1-butene
Isopentane
1-Pentene
2-Methyl-1-butene
n-Pentane
Isoprene
trans-2-Pentene
cis-2-Pentene
2-Methyl-2-butene
2,2-Dimethytbutane
Cyclopentene
4-Methyl-1-pentene
Cyclopentane
2,3-Dimethylbutane
2-Methylpentane
3-Methylpentane
2-Methyl-1 -pentene
1-Hexene
2-Ethy1-1-butene
n-Hexane
trans-2-Hexene
cis-2-Hexene
Methylcyclopentane
2,4-Dimethylpentane
Benzene
Cyclohexane
2-Methylhexane
2,3-Dimethytpentane
3-Methylhexane
1-Heptene
2,2,4-Trimethylpentane
n-Heptane
Methylcyclohexane
2,2,3-Trimethylpentane
2,3,4-Trimethylpentane
Toluene
2-Methylheptane
3-Methylheptane
1-Octene
n-Octane
Ethyl benzene
m-Xylene/p-Xylene
Styrene
o-Xylene
1-Nonene
n-Nonane
Isopropylbenzene
a-Pinene
n-Propyl benzene
m-Ethyltoluene
p-Ethyltoluene
1,3,5-Trimethylbenzene
o-Ethyltoluene
b-Pinene
1,2,4-Trimethyl benzene
1-Decene
n-Decane
1,2,3-Trimethylbenzene
m-Diethylbenzene
p-Diethyl benzene
1-Undecene
n-Undecane
1-Dodecene
n-Dodecane
1-Tridecene
n-Tridecane
16265
7/17/99
8/10/99
0.47
0.45
1.77
0.25
1.09
NO
0.19
0.11
ND
0.32
0.08
0.14
ND
0.23
0.07
0.04
0.23
1.33
0.13
0.09
0.05
0.12
0.12
ND
0.05
0.11
0.25
0.09
ND
ND
ND
0.12
ND
ND
0.10
0.08
0.17
10.01
0.19
0.11
0.07
0.02
0.07
0.06
0.06
ND
0.05
0.20
0.04
0.04
0.02
0.05
0.07
0.10
0.15
0.05
0.01
0.05
0.07
0.17
0.05
0.06
0.05
0.04
0.05
0.12
0.07
ND
0.04
0.03
0.04
0.02
0.01
0.04
0.010
0.01
0.00
0.010
162SS
7/23/99
8/10/99
0.47
0.39
1.14
0.25
0.89
ND
0.14
0.12
ND
0.25
0.07
0.12
ND
0.20
0.08
0.03
0.20
0.96
0.07
0.08
0.02
0.11
0.11
ND
0.05
0.10
0.15
0.09
0.01
0.01
ND
0.10
ND
ND
0.08
0.06
0.13
0.17
0.18
0.09
0.05
0.02
0.09
0.05
0.05
ND
0.04
0.20
0.04
0.04
0.01
0.05
0.05
0.11
0.18
0.05
ND
0.04
0.05
0.17
0.04
0.07
0.04
0.03
0.06
0.14
0.07
ND
0.03
0.03
0.04
0.03
0.01
0.03
0.011
0.01
0.00
0.012
16273
8/4/99
8/16/99
0.30
0.29
0.92
0.18
0.62
ND
0.10
0.10
ND
0.16
0.07
0.10
ND
0.16
0.06
0.02
0.19
0.22
0.05
0.07
0.02
0.11
0.03
ND
0.05
0.10
0.12
0.09
0.01
0.02
ND
0.10
ND
ND
0.07
0.06
0.10
0.14
0.16
0.10
0.05
0.01
0.06
0.04
0.05
ND
0.04
0.12
0.03
0.04
ND
0.05
0.04
0.07
0.11
0.04
ND
0.03
0.04
0.12
0.03
0.04
0.04
0.03
0.05
0.08
0.06
ND
0.03
0.03
0.05
0.02
ND
0.04
0.009
0.01
ND
0.013
16491
8/16/99
9/3/99
0.39
0.27
0.64
0.33
1.06
ND
0.16
0.09
ND
0.22
0.06
0.20
0.25
ND
0.06
ND
0.13
0.46
0.05
0.07
ND
0.10
0.03
ND
0.06
0.11
0.19
0.13
ND
ND
ND
0.13
ND
ND
0.06
0.07
0.13
0.22
0.19
0.11
0.25
ND
0.07
0.06
0.06
ND
0.05
0.21
0.05
0.04
0.01
0.06
0.26
0.37
0.27
0.14
0.01
0.05
0.05
0.08
0.05
0.08
0.05
0.03
0.06
0.17
0.06
ND
0.07
0.07
0.06
0.11
0.04
0.14
0.004
0.01
0.00
0.015
TNMOC (speciated), ppbv
TNMOC (w/ unknowns), ppbC
20.50
153.82
8.89
89.29
6.38
60.28
9.29
184.17
@ - Isopentane can not be quantitated in the 9/14/98 sample due to an analytical interference.
# - The QC recovery for n-Undecane was outside of QC criteria on 1/11/99. 10 of 11
-------
SNMOC OPTION REPORT
SITE CODE: UNVT
Rutland, VT
Reported in ppbv
SanvleNo.: 16611 16801 16890
Sampling Date: 8/28/99 9/9/99 9/21/99
Analysis Date: VOID 10/6/99 10/11/99
Compound
Ethylene 0.62 0.57
Acetylene 0.43 0.37
Ethane 1.63 1.07
Propylene 0.34 0.41
Propane 0.96 0.88
Propyne ND ND
Isobutane 0.28 0.18
lsobutene/1-Butene 0.13 0.13
1,3-Butadiene ND ND
n-Butane 0.30 0.24
trans-2-Butene 0.08 0.06
cis-2-Butene 0.09 0.10
3-Methyl-1-butene ND ND
Isopentane 0.80 0.18
1-Pentene 0.13 0.06
2-Methyl-1-butene 0.07 0.02
n-Pentane 0.36 0.12
Isoprene 0.32 0.08
trans-2-Pentene 0.06 0.07
cis-2-Pentene 0.07 0.07
2-Methyl-2-butene 0.02 0.03
2,2-Dimethylbutane 0.15 0.09
Cyclopentene • 0.03 0.03
4-Methyl-1-pentene ND ND
Cyclopentane 0.08 0.06
2,3-Dimethylbutane 0.10 0.09
2-Methylpentane 0.21 0.27
3-Methylpentane 0.13 0.10
2-Methyl-1-pentene 0.01 0.01
1-Hexene 0.07 0.01
2-Ethyl-1-butene 0.12 0.08
n-Hexane ND ND
trans-2-Hexene ND 0.01
cis-2-Hexene ND ND
Methylcyclopentane 0.07 0.05
2,4-Dimethylpentane 0.08 0.06
Benzene 0.15 0.13
Cyclohexane 10.17 0.09
2-Methylhexane 0.17 0.19
2,3-Dimethylpentane 0.10 0.10
3-Methylhexane 0.08 0.25
1-Heptene 0.05 0.01
2,2,4-Trimethylpentane 0.08 0.08
n-Heptene 0.06 0.05
Methylcyclohexane 0.05 0.07
2,2,3-Trimethylpentane ND ND
2,3,4-Trimethylpentane 0.05 0.05
Toluene 0.48 0.22
2-Methylheptane 0.07 0.05
3-Methylheptane 0.04 0.04
1-Octene ND 0.01
n-Octane 0.08 0.05
Ethylbenzene 0.33 0.27
m-Xylene/p-Xylene 0.25 0.29
Styrene 0.37 0.22
o-Xylene 0.15 0.13
1-Nonene 0.05 ND
n-Nonane 0.13 0.05
Isopropylbenzene 0.05 0.06
a-Pinene 0.13 ND
n-Propylbenzene 0.07 0.05
m-Ethyltoluene 0.10 0.07
p-Ethyltoluene 0.07 0.04
1,3,5-Trimethylbenzene 0.07 0.02
o-Ethyltoluene 0.06 0.04
b-Pinene 0.26 0.04
1,2,4-Trimethylbenzene ND ND
1-Decene 0.10 0.07
n-Decane 0.14 0.04
1.2,3-Trimethylbenzene 0.06 0.05
m-Diethylbenzene 0.11 0.10
p-Diethylbenzene 0.14 0.15
1-Undecene 0.03 0.02
n-Undecane 0.18 0.09
1-Dodecene 0.015 0.003
n-Dodecane 0.02 0.01
1-Tridecene ND ND
n-Tridecane 0.003 0.003
TNMOC (speciated). ppbv 22.26 8.69
TNMOC (w/unknowns), ppbC 296.65 191.28
! - Isopentane can not be quantitated in the 9/14/98 sample due to an analytical interference.
- The QC recovery for n-Undecane was outside of QC criteria on 1/11/99. 11 of 11
-------
APPENDIX G
1998/1999 CARBONYL RAW MONITORING DATA
-------
1998 UATMP CARBONYLS
Sample Site: Baton Rouge, LA
B2LA
SAMPLE* :
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
14781
9/8/98
10/28/98
Q8J-023
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
14896
9/20/98
11/12/98
Q8KK023
ppbv
1.11
0.60
0.01
0.70
0.10
ND
0.81
0.06
0.02
0.03
ND
0.03
ND
15065
10/2/98
11/16/98
Q8KP008
ppbv
1.63
0.61
0.05
0.46
0.09
ND
0.09
0.07
0.01
0.02
ND
0.02
0.02
15127
10/14/98
11/t6/98
Q8KP009
ppbv
3.76
1.68
0.03
2.91
0.23
ND
0.50
0.11
0.02
0.05
0.03
0.04
ND
15168
11/1/98
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15176
11/7/99
12/22/98
Q8LU019
ppbv
1.40
0.70
0.04
0.78
0.08
0.05
0.21
0.03
0.01
0.03
0.04
0.02
ND
15188
11/13/98
12/22/98
Q8LU027
ppbv
1.24
0.97
0.02
1.25
0.08
ND
0.27
0.05
0.02
0.02
ND
0.02
ND
u - Concentration is below the detection limit
1 of 6
-------
1998 UATMP CARBONYLS
Sample Site: Baton Rouge, LA
SAMPLE* :
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15204
11/19/98
12/22/98
Q8LU029
ppbv
1.52
1.10
0.01
0.74
0.15
ND
0.14
0.08
0.02
0.04
0.03
0.02
ND
15214
11/25/98
12/22/98
Q8LU033
ppbv
1.76
1.11
0.02
1.17
0.11
ND
0.17
0.05
0.03
0.04
0.04
0.02
ND
15244
12/1/98
12/22/98
Q8LU036
ppbv
1.40
0.82
0.01
0.79
0.08
ND
0.21
0.04
0.01
0.02
0.01
0.02
0.01
15366
1/30/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15369
1/30/99
3/16/99
09CO024
ppbv
0.72
0.36
ND
0.50
0.07
0.02
0.02
0.02
ND
0.02
0.02
0.01
ND
15436
2/11/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15438
2/17/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15468
2/25/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
u - Concentration is below the detection limit
-------
1998 UATMP CARBONYLS
Sample Site: Baton Rouge, LA
SAMPLE #
SAMPLE PATTE ,:- . - '•• •' --'•':
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15490
•'"-': 3fiV99 • "
.'• #17/9i9 " •
Q9l66b8
PpbV ;
0.73
0.56
ND
0.79
0.10
0.03
0.04
0.01
ND
0.01
0.02
0.02
ND
15510
3/13/99 :
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15533
: 3/19/99
4/1/99
O9C%030
ppbv
1.87
0.99
0.02
1.51
0.22
0.06
0.06
0.02
ND
0.04
0.02
0.07
ND
15673
4/19/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15696
4/20/99
5/20/99
O9ES020
ppbv
0.85
0.56
ND
0.40
0.07
0.01
0.04
0.02
ND
0.02
ND
0.02
ND
15698
4/20/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15708
4/26/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15760
4/30/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
u - Concentration is below the detection limit
3 of 6
-------
1998 UATMP CARBONYLS
Sample Site: Baton Rouge, LA
SAMPLE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Folualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15761
4/30/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15757
5/2/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15779
5/25/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15816
6/4/99
6/10/99
Q9FH031
ppbv
2.78
0.36
0.06
0.11
0.10
ND
0.26
0.02
ND
0.03
0.06
0.06
ND
15833
6/11/99
6/19/99
O9FR021
ppbv
1.67
0.47
ND
0.07
0.08
ND
0.27
0.03
0.01
0.04
0.06
0.07
ND
16040
7/5/99
8/6/99
O9HE013
ppbv
2.69
0.95
0.02
0.12
0.18
ND
0.21
0.05
0.02
0.09
0.04
0.17
ND
16134
7/23/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
16247
7/29/99
8/24/99
O9HX011
ppbv
1.89
0.68
ND
0.10
0.09
ND
0.09
0.03
0.01
0.05
0.04
0.08
ND
u - Concentration is below the detection limit
4 of 6
-------
1998 UATMP CARBONYLS
Sample Site: Baton Rouge, LA
SAMPLE #
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
16317
8/10/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
16476
8/22/99
9/11/99
O9IJ020
ppbv
1.21
0.46
0.01
0.07
0.08
ND
0.18
0.02
0.01
0.02
0.02
0.04
ND
16696
9/5/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
16722
9/15/99
10/1/99
O9I$036
ppbv
4.16
1.12
0.004
1.85
0.18
ND
0.19
0.07
0.01
0.03
0.05
0.03
ND
16870
9/27/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
u - Concentration is below the detection limit
5 of 6
-------
FIELD BLANK DATA
Sample site: Baton Rouge, LA
RAW AMOUNT
Derivatized Cone. (ug/mL)
Data File ID
FBID
Sample date
Date Analyzed
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyd<
Q8KK009
14897 FB
9/20/98
11/11/98
1.21
0.21
0.02
0.45
0.00
0.00
0.91
0.00
0.00
0.00
0.00
0.04
0.00
O9C%013
15534FB
3/19/99
3/31/99
2.14
1.95
0.00
3.91
0.31
0.09
0.05
0.00
0.00
0.00
0.09
0.03
0.00
VOID
15758FB
5/2/99
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15780FB
5/23/99
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
Field Blanks
Underivatized Conc.(total ug)
Data File ID
FBID
Date Analyzed
Q8KK009
14897FB
11/11/98
O9C%013
15534FB
3/31/99
VOID
15758FB
VOID
VOID
15780FB
VOID
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.69
0.16
0.02
0.44
ND
ND
1.04
ND
ND
ND
ND
0.06
ND
1.22
1.53
ND
3.81
0.30
0.10
0.06
ND
ND
ND
0.15
0.05
ND
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
6 of 6
-------
1998 UATMP CARBONYLS
Sample site: Beulah, ND
BUND
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15375D1
2/3/99
3/17/99
09CO076
ppbv
1.11
0.62
ND
1.72
0.05
ND
0.05
0.02
ND
0.04
0.02
0.09
ND
15375R1
2/3/99
3/17/99
09CO077
ppbv
1.10
0.63
ND
1.73
0.05
ND
0.04
0.02
ND
0.04
0.01
0.09
ND
15376 D2
2/3/99
3/17/99
09CO078
ppbv
1.01
0.76
0.04
3.71
0.06
ND
0.04
0.03
ND
0.06
0.02
0.18
ND
15376R2
2/3/99
3/17/99
09CO079
ppbv
1.05
0.76
0.04
3.70
0.06
ND
0.04
0.03
ND
0.06
0.02
0.18
ND
15408
2/13/99
3/16/99
09CO032
ppbv
0.98
0.58
ND
0.79
0.07
0.02
0.05
0.01
ND
0.05
0.02
0.10
ND
15430
2/17/99
3/16/99
09CO033
ppbv
0.88
0.56
ND
0.70
0.09
0.02
0.05
0.01
ND
0.04
0.02
0.03
ND
15442
2/23/99
3/16/99
09CO042
ppbv
0.88
0.47
ND
0.68
0.08
0.02
0.04
0.01
ND
0.03
0.02
0.05
ND
15452
3/1/99
3/17/99
O9CQ006
ppbv
0.76
0.43
ND
0.71
0.07
ND
0.02
ND
ND
0.02
0.02
0.09
ND
15498
3/7/99
3/17/99
O9CQ007
ppbv
0.81
0.48
ND
0.77
0.07
0.02
0.03
0.01
ND
0.04
0.02
0.05
ND
15538D1
3/13/99
4/1/99
O9C%038
ppbv
0.50
0.28
ND
0.54
0.04
0.01
0.02
0.003
0.002
0.03
ND
0.07
ND
u - Concentration is below the detection limit
1 of 7
-------
1998 UATMP CARBONYLS
Sample site: Beulah, ND
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
rolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15538R1
3/13/99
4/1/99
O9C%039
ppbv
0.50
0.28
ND
0.53
0.04
0.01
0.02
0.01
0.002
0.03
0.01
0.07
ND
15539D2
3/13/99
4/1/99
O9C%035
ppbv
1.05
0.59
ND
1.14
0.09
0.01
0.04
0.01
ND
0.05
0.01
0.07
ND
15539R2
3/13/99
4/1/99
O9C%036
ppbv
1.04
0.58
ND
1.13
0.09
0.01
0.04
0.01
ND
0.05
0.01
0.08
ND
15541 D1
3/19/99
4/1/99
O9C%042
ppbv
0.50
0.20
ND
0.34
0.03
0.01
0.01
ND
ND
0.01
0.01
0.06
ND
15541 R1
3/19/99
4/1/99
O9C%043
ppbv
0.50
0.20
ND
0.35
0.03
0.01
0.01
0.003
ND
0.02
0.01
0.06
ND
15543 D2
3/19/99
4/1/99
O9C%040
ppbv
1.00
0.52
ND
0.92
0.07
0.02
0.04
0.004
ND
0.04
0.01
0.07
ND
15543R2
3/19/99
4/1/99
O9C%041
ppbv
1.05
0.52
ND
0.92
0.07
0.02
0.04
0.01
ND
0.03
0.01
0.07
ND
15571
3/25/99
4/14/99
09DM027
ppbv
0.75
0.45
ND
0.78
0.07
ND
0.02
ND
ND
0.02
0.01
0.02
ND
15641
3/31/99
5/12/99
O9EK019
ppbv
0.64
0.41
ND
0.71
0.06
0.02
0.04
0.01
ND
0.02
ND
0.06
ND
15647
4/6/99
5/12/99
O9EK024
ppbv
0.79
0.43
ND
1.09
0.06
0.01
0.03
0.01
ND
0.02
ND
0.04
ND
u - Concentration is below the detection limi
2 of 7
-------
1998 UATMP CARBONYLS
Sample site: Beulah, ND
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15638
4/12/99
5/19/99
09ES016
ppbv
0.54
0.37
0.02
0.78
0.05
0.02
0.03
0.01
ND
0.02
ND
0.06
ND
15683D1
4/18/99
5/20/99
O9ES038
ppbv
0.72
0.48
ND
1.07
0.07
0.02
0.03
0.005
ND
0.02
ND
0.04
ND
15683 R1
4/18/99
5/20/99
O9ES039
ppbv
0.75
0.47
ND
1.06
0.07
0.02
0.03
0.007
ND
0.02
ND
0.04
ND
15685 D2
4/18/99
5/20/99
O9ES040
ppbv
0.29
0.22
ND
0.47
0.04
0.01
0.01
0.004
ND
0.01
ND
0.04
ND
15685R2
4/18/99
5/20/99
O9ES041
ppbv
0.29
0.22
ND
0.47
0.03
0.01
0.01
0.005
ND
0.01
ND
0.04
ND
15706
4/24/99
6/4/99
Q9FD015
ppbv
0.70
0.65
0.01
1.40
0.07
ND
0.29
ND
ND
ND
ND
0.08
ND
15713
4/30/99
6/4/99
Q9FD016
ppby
1.00
0.67
0.02
1.50
0.06
ND
0.40
ND
ND
0.02
ND
0.06
ND
15728
5/6/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15730
5/6/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15774
5/18/99
6/9/99
Q9FH018
ppbv
1.42
0.69
0.05
1.20
0.09
ND
0.43
0.03
0.025
0.07
0.06
0.10
ND
u - Concentration is below the detection limi
3 Of 7
-------
1998 UATMP CARBONYLS
Sample site: Beulah, ND
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15772
5/24/99
6/10/99
Q9FH022
ppbv
1.34
0.57
0.03
1.25
0.08
ND
0.46
0.03
0.032
0.04
ND
0.08
ND
15835
6/11/99
6/18/99
O9FR018
ppbv
1.23
0.49
0.04
0.89
0.07
0.01
0.08
0.03
0.01
0.04
0.02
0.09
ND
15900
6/17/99
7/7/99
O9GF017
ppbv
1.86
0.48
0.04
1.09
0.07
ND
0.09
0.04
ND
0.04
0.02
0.07
ND
15930
6/23/99
7/7/99
O9GF022
ppbv
1.76
0.61
0.05
1.47
0.09
ND
0.09
0.03
0.01
0.05
0.03
0.10
ND
15970
6/29/99
7/7/99
O9GF024
ppbv
1.15
0.52
0.03
1.12
0.07
0.01
0.07
0.05
0.01
0.04
0.02
0.06
ND
16004
7/5/99
8/6/99
O9HE014
ppbv
1.21
0.47
0.03
1.17
0.06
ND
0.04
0.02
ND
0.04
0.02
0.09
ND
16136
7/17/99
8/6/99
O9HE029
ppbv
1.27
0.56
0.03
0.95
0.08
ND
0.07
0.03
0.01
0.04
ND
0.08
ND
16147
7/23/99
8/6/99
O9HE034
ppbv
2.14
0.83
0.03
1.87
0.10
ND
0.12
0.05
0.012
0.05
0.02
0.07
ND
16204
7/29/99
8/6/99
09HE036
ppbv
3.50
1.77
0.04
3.46
0.22
0.01
0.21
0.07
0.04
0.09
0.03
0.14
ND
16282
8/4/99
8/24/99
O9HX013
ppbv
2.71
1.61
0.03
2.18
0.18
ND
0.20
0.07
0.03
0.08
0.03
0.11
ND
u - Concentration is below the detection limi
4af7
-------
1998 UATMP CARBONYLS
Sample site: Beulah, ND
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
16315
8/10/99
8/24/99
O9HX014
ppbv
3.44
1.30
0.04
1.91
0.15
ND
0.19
0.06
0.02
0.07
0.03
0.10
ND
16360
8/16/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
16441
8/22/99
9/11/99
O9IJ023
ppbv
2.45
0.86
0.03
1.83
0.10
ND
0.12
0.03
0.01
0.05
0.02
0.09
ND
16600
8/28/99
9/23/99
O9IV022
ppbv
2.21
0.85
0.04
1.45
0.10
ND
0.12
0.03
0.01
0.06
0.03
0.09
ND
16675
9/3/99
9/23/99
O9IV021
ppbv
1.35
0.80
0.06
1.06
0.07
ND
0.09
0.02
0.01
0.04
0.03
0.09
ND
16703
9/9/99
9/23/99
O9IV023
ppbv
1.33
0.48
0.03
1.73
0.05
ND
0.07
0.02
ND
0.04
0.02
0.07
ND
16787 01
9/15/99
10/2/99
O9I$053
ppbv
1.30
0.46
ND
1.78
0.06
ND
0.07
0.01
ND
0.04
ND
0.08
ND
16787 R1
9/15/99
10/2/99
O9I$054
ppbv
1.29
0.46
ND
1.78
0.06
0.01
0.08
0.02
ND
0.04
ND
0.07
ND
16789D2
9/15/99
10/2/99
09I$055
ppbv
1.28
0.44
ND
1.59
0.06
ND
0.07
0.01
ND
0.03
ND
0.06
ND
16789 R2
9/15/99
10/2/99
09I$056
ppbv
1.24
0.42
ND
1.53
0.06
ND
0.07
0.01
ND
0.03
ND
0.05
ND
16800
9/21/99
10/13/99
O9JM019
ppbv
1.63
0.72
0.02
2.20
0.10
0.01
0.12
0.03
0.01
0.04
ND
0.05
ND
u - Concentration is below the detection limi
5 Of 7
-------
1998 UATMP CARBONYLS
Sample site: Beulah, ND
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
16839 D1
9/27/99
10/14/99
O9JM026
ppbv
0.99
0.39
0.02
0.93
0.05
0.01
0.06
0.02
ND
0.03
0.02
0.05
ND
16839 R1
9/27/99
10/14/99
O9JM027
ppbv
1.02
0.39
0.02
0.96
0.05
0.01
0.06
0.02
ND
0.03
0.02
0.06
ND
16841 D2
9/27/99
10/14/99
O9JM028
ppbv
1.10
0.38
0.02
0.88
0.05
0.01
0.07
0.02
0.01
0.02
0.02
0.04
ND
16841 R2
9/27/99
10/14/99
O9JM029
ppbv
1.10
0.38
0.01
0.88
0.05
0.01
0.07
0.02
0.01
0.03
0.01
0.04
ND
u - Concentration is below the detection limi
-------
FIELD BLANK DATA
Sample site: Beulah, ND
RAW AMOUNT
Derivatized Cone. (ug/mL)
Data File ID
FBID
Sample date
Date Analyzed
09ES007
15639FB
4/12/99
5/19/99
Q9FD008
1571 4 FB
4/30/99
6/4/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldeh
0.02
0.08
0.05
0.14
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.10
0.10
0.00
0.00
0.29
0.05
0.29
0.00
0.00
0.00
0.00
0.05
0.00
Q9FH009
15775FB
5/18/99
6/9/99
0.08
0.10
0.00
0.17
0.00
0.00
0.39
0.00
0.00
0.00
0.00
0.00
0.00
Field Blanks
Underivatized Conc.(total ug)
Data File ID
FBID
Date Analyzed
O9ES007
15639FB
5/19/99
Q9FD008
1571 4 FB
6/4/99
Q9FH009
15775 FB
6/9/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldeh
0.01
0.07
0.05
0.14
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.05
0.08
ND
0.00
0.29
0.05
0.33
ND
ND
ND
ND
0.07
ND
0.05
0.08
ND
0.17
ND
ND
0.45
ND
ND
ND
ND
ND
ND
7 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Brattleboro, Vermont
BRVT
Derivatized Cone;. (ug/mL)
SAMPLE DAW '•••^ " '
ANAL*§(S JDATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
14685
9/2/98
10/27/98
Q8J-012
ppbv
1.22
0.44
0.02
0.79
0.07
ND
0.24
0.04
0.01
0.02
0.02
0.04
ND
14812
9/14/98
10/28/98
Q8J-029
ppbv
1.56
0.79
0.09
0.90
0.10
ND
0.11
0.07
0.01
0.03
0.04
0.05
ND
15055
9/26/98
11/12/98
Q8KK024
ppbv
1.41
0.71
ND
1.16
0.09
ND
0.11
0.08
0.02
0.03
0.04
0.06
ND
15114
10/8/98
11/16/98
Q8KP012
ppbv
1.08
0.66
0.05
0.69
0.08
ND
0.27
0.03
0.01
0.03
ND
0.03
ND
15138
10/20/98
11/16/98
Q8KP013
ppbv
1.00
0.52
ND
1.18
0.07
ND
0.27
0.03
ND
0.02
ND
0.03
ND
15156
11/1/98
11/25/98
Q8KW021
ppbv
0.72
0.36
0.01
0.86
0.05
ND
0.28
0.03
ND
0.02
0.02
0.03
ND
15196
11/13/98
11/25/98
Q8KW025
ppbv
1.17
0.75
0.03
1.33
0.09
ND
0.22
0.05
0.015
0.02
0.03
0.03
0.01
u - Concentration is below the detection limit
1 QL7
-------
1998 UATMP CARBONYLS
Sample Site: Brattleboro, Vermont
Derivatized Cone. (ug/mL) :
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15238
11/25/98
12/21/98
Q8LU010
ppbv
1.11
0.56
0.02
1.16
0.07
ND
0.11
0.05
0.01
0.02
0.03
0.03
ND
15252
12/7/98
12/21/98
Q8LU014
ppbv
1.12
0.74
0.01
0.94
0.10
0.04
0.13
0.03
0.02
0.03
0.03
0.03
ND
15283
12/19/98
1/8/99
O9AG034
ppbv
1.32
0.87
0.04
1.12
0.10
0.01
0.14
0.05
0.01
0.02
0.04
0.03
ND
15305
12/31/98
2/20/99
O9BS016
ppbv
2.26
1.17
0.05
1.42
0.12
0.03
0.19
0.07
0.02
0.04
0.05
0.05
ND
15319
1/12/99
2/20/99
O9BS022
ppbv
1.69
1.08
0.03
1.40
0.13
0.02
0.13
0.07
0.01
0.03
0.06
0.05
ND
15350D1
1/24/99
2/20/99
O9BS027
ppbv
0.88
0.56
0.01
0.72
0.06
0.01
0.06
0.04
0.01
0.02
0.02
0.03
ND
15350R1
1/24/99
2/20/99
O9BS028
ppbv
0.90
0.57
0.01
0.74
0.06
0.01
0.06
0.04
0.01
0.02
0.02
0.03
ND
u - Concentration is below the detection limit
2 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Brattleboro, Vermont
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15352D2
1/24/99
2/20/99
O9BS029
ppbv
0.93
0.58
0.01
0.75
0.06
0.01
0.06
0.04
0.010
0.02
0.03
0.04
ND
15352 R2
1/24/99
2/20/99
O9BS030
ppbv
0.89
0.58
0.01
0.75
0.06
0.01
0.06
0.05
0.01
0.02
0.03
0.04
ND
15414
2/5/99
3/16/99
09CO026
ppbv
0.83
0.41
ND
0.71
0.08
0.04
0.03
0.02
ND
0.04
0.03
0.02
ND
15444
2/15/99
3/16/99
09CO034
ppbv
1.47
0.96
ND
2.62
0.15
0.12
0.07
0.06
ND
0.04
0.06
0.06
ND
15484
3/1/99
3/16/99
09CO051
ppbv
1.36
0.71
ND
1.09
0.11
0.09
0.05
0.04
ND
0.04
0.05
0.05
ND
15548
3/13/99
3/31/99
O9C%020
ppbv
1.02
0.54
ND
0.76
0.10
0.03
0.05
0.04
ND
0.03
0.02
0.03
ND
15588D1
3/25/99
4/14/99
O9DM044
ppbv
0.93
0.42
ND
0.78
0.07
ND
0.03
0.02
ND
0.02
0.02
0.02
ND
u - Concentration is below the detection limit
3 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Brattleboro, Vermont
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15588R1
3/25/99
4/14/99
O9DM045
ppbv
0.95
0.43
ND
0.79
0.07
ND
0.03
0.02
ND
0.02
0.02
0.02
ND
1559002
3/25/19
4/14/99
O9DM046
ppbv
0.93
0.40
ND
0.75
0.07
ND
0.03
0.02
ND
0.02
0.02
0.02
ND
15590 R2
3/25/99
4/14/91
O9DM048
PpbV
0.93
0.40
ND
0.75
0.07
ND
0.03
0.02
ND
0.02
0.02
0.02
ND
15657
4/6^9 v;:
5/12/9$
O9EK025
ppbv
1.57
0.80
ND
1.37
0.12
0.04
0.06
0.03
ND
0.02
0.00
0.04
ND
15827
5/12799
'•- •-• . v. ••--• '-
V0ID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15829
5/12/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15790
5/18/99
6/9/99
Q9FH019
ppbv
1.83
1.14
0.04
0.76
0.13
ND
0.26
0.06
0.047
0.05
0.04
0.11
ND
u - Concentration is below the detection limit
4 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Brattleboro, Vermont
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15837
5/30/99
6/18/99
O9FR013
ppbv
3.54
1.51
0.04
1.41
0.24
0.01
0.19
0.16
0.032
0.10
0.06
0.17
0.00
15839
6/5/99
6/18/99
O9FR014
ppbv
2.50
0.96
0.02
2.01
0.15
0.01
0.16
0.13
0.02
0.06
0.07
0.11
ND
15920
6/17/99
7/7/99
O9GF016
ppbv
2.23
0.73
0.01
1.50
0.11
ND
0.13
0.09
0.02
0.04
0.05
0.06
ND
16023
6/29/99
8/5/99
O9HE009
ppbv
1.94
0.78
0.01
0.22
0.08
ND
0.07
0.04
0.02
0.05
0.04
0.06
ND
16270
7/17/99
8/19/99
O9HQ025
ppbv
2.93
0.72
0.02
0.18
0.14
ND
0.15
0.06
0.03
0.11
0.06
0.14
ND
16253
7/23/99
8/19/99
O9HQ030
ppbv
3.55
1.12
ND
1.35
0.16
0.01
0.18
ND
ND
0.08
0.07
0.11
ND
16311
8/2/99
8/24/99
O9HX012
ppbv
3.15
0.82
ND
1.72
0.09
ND
0.17
0.16
0.02
0.07
0.07
0.08
ND
u - Concentration is below the detection limit
-------
1998 UATMP CARBONYLS
Sample Site: Brattleboro, Vermont
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
16497
8/16/99
9/11/99
O9IJ016
ppbv
1.85
0.60
ND
1.15
0.08
ND
0.14
0.04
ND
0.04
0.04
0.06
ND
16612
8/28/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
16614
9/3/99
9/23/99
O9IV027
ppbv
2.82
0.73
ND
1.26
0.12
ND
0.11
0.06
0.01
0.05
0.05
0.08
ND
16804
9/9/99
10/1/99
O9I$034
ppbv
2.76
0.89
ND
0.81
0.10
ND
0.09
0.04
ND
0.04
0.03
0.08
ND
16904
9/21/99
10/13/99
O9JM011
ppbv
1.08
0.46
0.01
0.59
0.07
0.01
0.10
0.04
ND
0.03
0.05
0.05
0.01
u - Concentration is below the detection limit
6 of 7
-------
FIELD BLANK DATA
Sample site: Brattleboro, VT
RAW AMOUNT
Derivatized Cone. (ug/mL)
Data File ID
FBID
Sample date
Date Analyzed
Q8J-008
1481 3 FB
9/14/98
10/27/98
O9C%008
15549FB
3/13/99
3/31/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.03
0.05
0.00
0.34
0.00
0.00
0.28
0.00
0.00
0.00
0.00
0.02
0.00
0.19
0.10
0.03
0.17
0.02
0.00
0.01
0.04
0.00
0.01
0.02
0.03
0.00
Field Blanks
Underivatized Cone.(total ug)
Data File ID
FBID
Date Analyzed
Q8J-008
1481 3 FB
10/27/98
O9C%008
15549FB
3/31/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.02
0.04
ND
0.33
ND
ND
0.33
ND
ND
ND
ND
0.02
ND
0.11
0.08
0.03
0.16
0.02
ND
0.01
0.06
ND
0.02
0.03
0.05
ND
7 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Burlington, VT
BUVT
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
14678
9/2/98
10/27/98
Q8J-013
ppbv
2.56
0.85
0.10
1.00
0.10
ND
0.11
0.05
ND
0.02
0.04
0.01
ND
14819
9/14/98
10/29/98
Q8J#019
ppbv
1.86
0.79
0.20
0.66
0.09
ND
0.10
0.06
0.01
0.03
0.04
0.02
ND
15084
9/26/98
11/12/98
Q8KK025
ppbv
2.68
1.17
ND
1.03
0.13
ND
0.18
0.06
0.02
0.04
0.04
0.04
0.02
15108
10/8/98
11/16/98
Q8KP014
ppbv
2.67
0.98
0.03
1.19
0.12
0.05
0.48
0.08
ND
0.03
0.05
0.03
0.01
15148
10/20/98
11/16/98
Q8KP016
ppbv
3.10
0.83
0.02
1.89
0.11
ND
0.41
0.06
ND
0.02
0.04 i
0.02
ND
15154
11/1/98
11/25/98
Q8KW022
ppbv
1.97
0.72
0.03
1.07
0.07
ND
0.34
0.06
0.02
0.02
0.04
0.02
0.01
15198
11/13/98
11/25/98
Q8KW027
ppbv
2.75
0.87
0.02
1.60
0.09
ND
0.17
0.06
ND
0.03
0.06
0.02
0.02
15236
11/25/98
12/21/98
Q8LU011
ppbv
1.62
0.59
0.02
0.88
0.07
0.03
0.10
0.04
0.01
0.02
0.03
0.02
ND
15250
12/7/98
12/22/98
Q8LU016
ppbv
1.87
0.69
0.02
1.22
0.09
ND
0.12
0.05
0.01
0.02
0.04
0.02
ND
u - Concentration is below the detection limit
1 of 6
-------
1998 UATMP CARBONYLS
Sample Site: Burlington, VT
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Folualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15285
12/19/98
1/8/99
09AG035
ppbv
1.65
0.90
0.04
0.93
0.10
0.004
0.11
0.05
0.01
0.02
0.03
0.02
ND
15311
12/31/98
2/20/99
O9BS017
ppbv
1.66
1.01
0.03
0.90
0.11
0.01
0.09
0.06
0.01
0.03
0.03
0.03
0.003
15327
1/12/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15355D1
1/24/99
2/20/99
O9BS031
ppbv
2.01
0.75
0.01
0.84
0.09
0.01
0.08
0.05
0.01
0.02
0.04
0.04
ND
15355 R1
1/24/99
2/20/99
O9BS032
ppbv
2.01
0.75
0.01
0.84
0.09
0.004
0.07
0.05
0.01
0.02
0.04
0.04
ND
15357D2
1/24/99
2/20/99
O9BS033
ppbv
2.04
0.73
0.01 .
0.82
0.08
0.005
0.08
0.04
0.01
0.02
0.04
0.03
ND
15357R2
1/24/99
2/20/99
O9BS034
ppbv
2.04
0.73
0.01
0.82
0.09
0.005
0.08
0.05
0.009
0.02
0.04
0.04
ND
15406
2/5/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15450
2/17/99
3/16/99
09CO035
ppbv
2.53
1.03
ND
1.23
0.16
0.11
0.06
0.07
ND
0.03
0.05
0.02
ND
u - Concentration is below the detection limit
2 of 6
-------
1998 UATMP CARBONYLS
Sample Site: Burlington, VT
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15478
2/23/99
3/16/99
09CO043
ppbv
2.16
0.94
ND
0.93
0.15
0.10
0.05
0.05
ND
0.03
0.04
0.02
ND
15482
3/1/99
3/16/99
09CO052
ppbv
2.90
1.06
ND
1.15
0.17
ND
0.06
0.07
ND
ND
0.07
0.04
ND
15554
3/13/99
3/31/99
O9C%021
ppbv
2.20
0.77
ND
0.83
0.12
0.05
0.04
0.03
ND
0.02
0.02
0.01
ND
15603 D1
3/25/99
5/12/99
O9EK033
ppbv
2.19
0.57
ND
0.98
0.08
0.05
0.03
0.04
ND
0.01
0.02
0.02
ND
15603R1
3/25/99
5/12/99
O9EK034
ppbv
2.20
0.57
ND
0.96
0.08
0.05
0.03
0.04
ND
0.01
0.02
0.01
ND
15605D2
3/25/99
5/12/99
O9EK035
ppbv
2.01
0.54
ND
0.91
0.07
0.04
0.03
0.04
ND
0.01
0.02
0.01
ND
15605R2
3/25/99
5/12/99
O9EK036
ppbv
2.01
0.54
ND
0.91
0.07
0.04
0.03
0.04
ND
0.01
0.02
0.01
0.004
15645
4/6/99
5/12/99
O9EK027
ppbv
3.16
1.12
ND
1.28
0.16
0.08
0.08
0.05
ND
0.02
0.02
0.03
ND
15677
4/18/99
5/19/99
O9ES017
ppbv
2.47
0.74
ND
0.94
0.11
0.08
0.07
0.04
ND
0.02
0.01
0.02
ND
u - Concentration is below the detection limit
3 Of 6
-------
1998 UATMP CARBONYLS
Sample Site: Burlington, VT
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Folualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15734
4/30/99
6/5/99
Q9FD017
ppbv
4.99
1.67
0.02
2.02
0.20
ND
0.59
0.15
0.04
0.04
0.08
0.11
0.01
15796D1
5/12/99
6/10/99
Q9FH036
ppbv
3.25
1.05
0.02
1.69
0.13
ND
0.29
0.07
0.02
0.03
0.06
0.02
ND
15796R1
5/12/99
6/10/99
Q9FH037
ppbv
3.25
1.09
0.04
1.69
0.11
ND
0.31
0.07
0.04
0.03
0.09
0.02
ND
15798D2
5/12/99
6/10/99
Q9FH038
ppbv
3.52
1.13
0.02
1.75
0.14
ND
0.29
0.08
ND
0.04
0.07
0.04
ND
15798 R2
5/12/99
6/10/99
Q9FH039
ppbv
3.54
1.09
0.02
1.78
0.14
ND
0.27
0.06
0.02
0.04
0.07
0.04
0.01
15794
5/24/99
6/10/99
Q9FH023
ppbv
3.26
1.04
0.02
1.24
0.12
ND
0.50
0.07
0.02
0.04
0.04
0.05
ND
15841
6/5/99
6/18/99
O9FR016
ppbv
4.43
1.43
ND
2.26
0.20
ND
0.20
0.11
0.02
0.05
0.05
0.05
0.01
15922
6/17/99
7/7/99
O9GF018
ppbv
4.34
1.09
0.03
1.99
0.15
ND
0.15
0.09
0.01
0.04
0.05
0.04
0.01
16025
6/29/99
8/5/99
O9HE010
ppbv
1.72
0.07
0.006
0.08
0.02
ND
ND
0.06
ND
0.02
0.04
0.02
ND
u - Concentration is below the detection limit
4. Qf 6
-------
1998 UATMP CARBONYLS
Sample Site: Burlington, VT
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
16261
7/17/99
8/19/99
09HQ027
ppbv
5.59
1.63
0.03
0.18
0.25
0.01
0.19
0.05
0.02
0.06
0.06
0.08
ND
16263
7/29/99
8/19/99
09HQ031
ppbv
6.52
1.47
0.02
0.28
0.21
0.02
0.23
0.16
0.03
0.07
0.06
0.06
ND
16278
8/4/99
8/24/99
O9HX015
ppbv
2.75
1.06
0.09
0.39
0.14
ND
0.22
0.06
0.02
0.04
0.04
0.03
0.009
16495
8/16/99
9/11/99
O9IJ017
ppbv
4.18
1.38
ND
1.50
0.17
ND
0.23
0.08
0.03
0.07
0.06
0.06
ND
16616
8/28/99
9/23/99
09IV025
ppbv
4.61
1.01
ND
0.57
0.18
ND
0.13
0.06
ND
0.05
0.05
0.06
ND
16806
9/9/99
10/1/99
O9I$038
ppbv
3.39
1.00
0.01
1.32
0.12
ND
0.12
0.11
ND
0.06
0.06
0.06
ND
16902
9/21/99
10/13/99
O9JM012
ppbv
1.19
0.50
0.03
0.62
0.07
0.01
0.07
0.05
ND
0.03
0.05
0.03
ND
u - Concentration is below the detection limit
5 of 6
-------
FIELD BLANK DATA
Sample site: Burlington, VT
RAW AMOUNT
Derivatized Cone. (ug/mL)
Data File ID
FBID
Sample date
Date Analyzed
Q8J#008
14820FB
9/14/98
10/29/98
09C%009
15555FB
3/13/99
3/31/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethyibenzaldehyde
0.03
0.21
0.00
0.38
0.00
0.00
0.32
0.00
0.00
0.00
0.00
0.00
0.00
0.12
0.10
0.05
0.16
0.04
0.00
0.00
0.00
0.00
0.01
0.02
0.00
0.00
Field Blanks
Underivatized Cone, (total ug)
Data File ID
FBID
Date Analyzed
Q8J#008
14820FB
10/29/98
O9C%009
15555FB
3/31/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.02
0.17
ND
0.38
ND
ND
0.36
ND
ND
ND
ND
ND
ND
0.07
0.08
0.04
0.15
0.04
ND
ND
ND
ND
0.01
0.04
ND
ND
6 of 6
-------
1998 UATMP CARBONYLS
Sample Site: Camden, NJ
CANJ
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
14770
9/8/98
10/28/98
Q8J-024
ppbv
2.46
1.20
0.02
1.46
0.19
ND
0.54
0.04
0.02
0.27
ND
0.07
ND
14890
9/14/98
10/28/98
Q8J-030
ppbv
3.95
1.67
0.08
1.19
0.32
ND
0.49
0.10
0.02
0.23
0.02
0.10
ND
14970
9/20/98
11/12/98
Q8KK033
ppbv
3.80
2.44
0.20
1.26
0.39
ND
0.39
0.09
0.02
0.28
0.04
0.07
ND
15086
10/2/98
11/16/98
Q8KP017
ppbv
3.20
1.77
0.03
3.01
0.36
ND
1.09
0.05
0.04
0.55
0.03
0.12
ND
15121
10/14/98
11/16/98
Q8KP018
ppbv
2.03
1.19
0.03
1.93
0.18
ND
0.77
0.04
ND
0.18
ND
0.05
ND
15144
10/26/98
11/25/98
Q8KW014
ppbv
4.37
2.71
0.06
3.73
0.45
ND
1.23
0.12
0.04
0.64
0.04
0.14
ND
15178
11/7/98
12/22/98
Q8LU020
ppbv
2.64
1.96
0.04
2.10
0.37
0.04
0.71
0.07
0.059
0.62
0.06
0.05
0.02
u - Concentration is below the detection limit
1 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Camden, NJ
Derivatized Cone. (ug/mL) :;
iAMPLESATE .?::•' ;' "• ;;:'V- "':
ANALYSIS PATE
FILENAiViE
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15212
;H/19/$8
12/22/$8
Q8Ltib36
ppbv
2.78
1.87
0.02
3.13
0.29
ND
0.63
0.06
0.04
0.43
0.04
0.03
ND
15218
12/1/9:8 :
VOID
;;;- vciici
PPPV
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15228
12/11/98
12/22/98
Q8LU034
ppbv
1.92
1.18
0.02
1.75
0.12
ND
0.26
0.04
0.01
0.03
ND
0.06
ND
15263
12/13/98
1/8/99
O9AG028
ppbv
2.81
1.81
0.02
2.28
0.36
0.02
0.59
0.09
0.04
0.52
0.05
0.18
ND
15277
12/25/98
1/8/99
O9AG039
ppbv
3.23
1.95
0.04
1.96
0.48
0.02
0.71
0.05
0.03
0.68
0.04
0.17
ND
15317
1/6/99
2/20/99
O9BS020
ppbv
2.46
1.53
0.02
1.68
0.41
0.02
0.51
0.05
0.03
0.46
0.04
0.13
ND
u - Concentration is below the detection limit
2_of7
-------
1998 UATMP CARBONYLS
Sample Site: Camden, NJ
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
sovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15378D1
1/30/99
2/20/99
09BS044
ppbv
2.39
1.18
0.005
1.93
0.22
0.01
0.33
0.05
0.01
0.25
0.05
0.09
ND
15378R1
1/30/99
2/20/99
O9BS045
ppbv
2.39
1.18
0.005
1.93
0.21
0.01
0.33
0.05
0.02
0.25
0.05
0.09
ND
15380D2
1/30/99
2/20/99
O9BS046
ppbv
2.30
1.13
0.005
1.83
0.20
0.01
0.31
0.05
0.01
0.23
0.05
0.08
ND
15380R2
1/30/99;
2/20/99
O9BS047
ppbv
2.31
1.14
0.005
1.83
0.20
0.01
0.31
0.05
0.02
0.23
0.04
0.07
ND
15454
2/17/99
3/16/99
09CO049
ppbv
3.68
1.78
ND
2.92
0.34
0.12
0.26
0.06
0.05
0.23
0.09
0.10
ND
15464
2/23/99
3/16/99
09CO045
ppbv
2.75
1.56
ND
2.79
0.40
0.06
0.49
0.04
0.09
0.49
0.04
0.13
ND
15512
3/7/99
3/17/99
O9CQ009
ppbv
2.44
1.11
ND
1.33
0.24
0.05
0.25
0.02
0.05
0.23
0.02
0.05
ND
u - Concentration is below the detection limit
3 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Camden, NJ
Derivatized Cone. (ug/mL) ••.;. :.;:•:•
|A;MRLE':iATE::\'"^-.:vy.'::--; - ' i^—' ' •
ANALVSIS lijATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
1553(5
3/13799
21/31/99
O9C36022.
ppbv
3.11
1.30
ND
1.65
0.31
0.04
0.34
0.04
0.06
0.32
ND
0.06
ND
1562501
•3125199
5/12/99
09EK038
ppbv
2.50
1.12
0.04
1.96
0.23
0.04
0.21
0.02
ND
0.14
0.001
0.05
ND
15625R1
3/25/99
5/12/99
O9EK039
ppbv
2.57
1.12
0.04
1.96
0.23
0.04
0.22
0.02
ND
0.13
0.002
0.05
ND
15627 D2
3/25/99
5/12/99
O9EK040
ppbv
2.51
1.11
0.02
1.95
0.23
0.03
0.21
0.03
ND
0.12
0.004
0.05
ND
15627R2
3/25/99
5/12/99
O9EK041
ppbv
2.57
1.12
0.02
1.96
0.23
0.03
0.21
0.03
ND
0.12
0.003
0.05
ND
15687
4/18/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15710
4/30/99
6/5/99
Q9FD018
ppbv
1.51
0.82
0.01
1.72
0.12
ND
0.36
0.03
ND
0.12
0.04
0.07
ND
u - Concentration is below the detection limit
4 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Camden, NJ
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15787
5/24/99
6/10/99
Q9FH024
ppbv
3.69
2.16
0.03
2.09
0.36
ND
1.10
0.11
0.112
0.50
0.07
0.11
ND
15903
6/5/99
7/6/99
O9GF013
ppbv
4.76
2.32
0.02
2.97
0.44
0.01
0.50
0.11
0.03
0.35
0.04
0.15
ND
15996
6/17/99
7/28/99
O9GI014
ppbv
2.49
1.58
ND
2.57
0.49
ND
0.59
0.08
0.03
0.51
0.03
0.20
ND
16001
7/5/99
8/6/99
O9HE016
ppbv
8.75
3.13
0.04
1.43
0.74
ND
0.89
0.23
0.05 ,
0.78
0.06
0.29
ND
16037
7/11/99
8/6/99
O9HE020
ppbv
4.03
1.81
0.02
2.11
0.55
ND
0.70
0.09
0.04
0.67
ND
0.23
ND
16188
7/23/99
8/6/99
O9HE035
ppbv
8.02
3.25
0.04
1.80
0.69
0.02
0.54
0.13
0.03
0.30
0.07
0.14
ND
16242
8/4/99
8/24/99
09HX016
ppbv
5.73
2.69
0.02
1.13
0.48
0.01
0.54
0.13
0.04
0.34
0.09
0.15
ND
u - Concentration is below the detection limit
5 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Camden, NJ
Derivatized Cone. (ug/mL)
SAMPLE DATE r
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
16364
8/i&99
:l#5l99
d9ri*bl7
ppbv
5.33
2.62
0.02
0.94
0.50
0.01
0.54
0.17
0.03
0.40
0.07
0.15
ND
16602
8/28/99
9/23/99
O9IV019
ppbv
6.08
2.85
0.03
0.94
0.57
0.03
0.53
0.08
0.03
0.40
0.03
0.15
0.01
16714
9/9/99
9/23/99
O9IV020
ppbv
3.99
2.10
0.04
1.55
0.42
0.02
0.53
0.09
0.03
0.33
0.03
0.16
ND
16792 01
9/15/99
10/2/99
O9I$048
ppbv
2.87
1.71
ND
1.21
0.37
ND
0.38
0.08
0.03
0.31
0.03
0.13
ND
16792 R1
9/15/99
10/2/99
O9IS049
ppbv
2.87
1.64
ND
1.21
0.37
ND
0.35
0.05
0.04
0.31
0.03
0.13
ND
16793 D2
9/15/99
10/2/99
O9I$051
ppbv
2.79
1.67
ND
1.26
0.36
0.005
0.35
0.05
0.02
0.30
0.04
0.12
ND
16793R2
9/15/99
10/2/99
O9I$052
ppbv
2.85
1.65
ND
1.27
0.37
0.01
0.36
0.06
0.03
0.31
0.04
0.13
ND
u - Concentration is below the detection limit
6 Of 7
-------
FIELD BLANK DATA
Sample site: Camden, NJ
RAW AMOUNT
Derivatized Cone. (ug/mL)
Data File ID
FBID
Sample date
Date Analyzed
Q8J-009
14891 FB
9/14/98
10/27/98
Q8KK010
14971 FB
9/20/98
11/11/98
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.09
0.07
0.00
0.35
0.00
0.00
0.46
0.00
0.00
0.00
0.00
0.02
0.00
0.15
0.08
0.00
0.41
0.00
0.00
0.69
0.00
0.00
0.00
0.00
0.00
0.00
Q8KK018
15087FB
10/2/98
11/12/98
0.07
0.07
0.00
0.36
0.00
0.00
0.56
0.00
0.00
0.00
0.00
0.02
0.00
Q9FD009
15711 FB
4/30/99
6/4/99
Q9FH011
15788FB
5/24/99
6/9/99
0.05
0.10
0.00
0.00
0.22
0.04
0.27
0.00
0.04
0.00
0.00
0.16
0.00
0.28
0.15
0.00
0.28
0.00
0.00
0.63
0.00
0.00
0.00
0.00
0.00
0.00
O9GI008
16038FB
7/11/99
6/19/97
09HX007
16243 FB
8/4/99
7/15/97
0.09
0.06
0.00
0.10
0.00
0.00
0.05
0.02
0.02
0.02
0.00
0.01
0.00
0.08
0.06
0.00
0.09
0.01
0.00
0.00
0.00
0.00
0.02
0.00
0.02
0.00
O9IV007
16603 FB
8/28/99
7/31/97
0.07
0.14
0.00
0.16
0.01
0.00
0.00
0.02
0.00
0.02
0.00
0.03
0.00
Field Blanks
Underivatized Conc.(tota) ug)
Data File ID
FBID
Date Analyzed
Q8J-009
14891 FB
10/27/98
Q8KK010
14971 FB
11/11/98
Q8KK018
15087FB
11/12/98
Q9FD009
15711 FB
6/4/99
Q9FH011
15788 FB
6/9/99
O9GI008
16038FB
6/19/97
09HX007
16243FB
7/15/97
O9IV007
16603 FB
7/31/97
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.05
0.05
ND
0.34
ND
ND
0.53
ND
ND
ND
ND
0.03
ND
0.09
0.07
ND
0.40
ND
ND
0.79
ND
ND
ND
ND
ND
ND
0.04
0.06
ND
0.35
ND
ND
0.64
ND
ND
ND
ND
0.03
ND
0.03
0.08
ND
0.00
0.21
0.05
0.31
ND
0.05
ND
ND
0.23
ND
0.16
0.12
ND
0.27
ND
ND
0.72
ND
ND
ND
ND
ND
ND
0.07
0.06
ND
0.13
ND
ND
0.08
0.03
0.03
0.03
ND
0.02
ND
0.06
0.06
ND
0.10
0.01
ND
ND
ND
ND
0.03
ND
0.04
ND
0.05
0.14
ND
0.20
0.02
ND
ND
0.04
ND
0.04
ND
0.05
ND
7 of 7
-------
1998 UATMP CARBONYLS
Sample Site: El Paso, TX
EPTX
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
14894
9/14/98
10/29/98
Q8J#020
ppbv
14.32d
4.83
0.12
1.60
0.31
0.02
0.40
0.33
0.33
0.16
0.26
0.23
0.02
15001
9/20/98
11/12/98
Q8KK034
ppbv
3.68
1.34
0.03
1.18
0.14
ND
0.34
0.07
0.01
0.04
0.03
0.03
0.01
15067
10/2/98
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15129
10/2/98
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15130
10/14/98
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15150
10/26/98
11/25/98
Q8KW016
ppbv
20.13d
4.36
0.40
0.72
0.25
0.05
0.42
0.38
0.32
0.19
0.31
0.25
0.02
15184
11/7/98
12/22/98
Q8LU021
ppbv
1 1 .84d
2.23
0.11
1.92
0.12
0.02
0.23
0.20
0.18
0.10
0.25
0.15
0.02
15208
11/19/98
12/22/98
Q8LU028
ppbv
3.44
1.10
0.03
1.33
0.10
ND
0.14
0.07
0.04
0.05
0.05
0.02
0.02
u - Concentration is below the detection limit
d - Concentration determined using a
dilution factor
1 of 7
-------
1998 UATMP CARBONYLS
Sample Site: El Paso, TX
Derivatized Cone. (ug/mL)
lAtoPLiEpAT E "< :•; " '' " '••.;' ; ." •'•'•'. '"
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15234
12/1/98 :
12/22/93
Q8LU035
ppby
2.94
1.19
0.02
1.48
0.11
ND
0.14
0.08
0.02
0.03
0.05
0.01
ND
15267
12713/08
1/8&I
O9AG029
ppbv
4.09
2.42
0.04
2.25
0.26
0.02
0.22
0.11
0.01
0.05
0.10
0.05
ND
15291
12/25/98
1/8/99
D9AG040.'
ppbv
5.38
2.43
0.05
2.57
0.25
0.02
0.24
0.13
0.02
0.07
0.13
0.06
ND
15344
i 1/6/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID ,
VOID
VOID
15390
1^30/99
3/16/99
09(C6623
ppbv
2.80
1.20
ND
1.32
0.17
0.07
0.07
0.06
ND
0.04
0.05
0.03
ND
15402D1
2/11/99
3/16/99
09CO063
ppbv
1.46
0.54
ND
0.51
0.08
0.05
0.03
0.02
ND
0.02
0.03
0.01
ND
15402R1
2/11/99
3/16/99
09CO064
ppbv
1.48
0.54
ND
0.51
0.09
0.05
0.03
0.03
ND
0.03
0.03
0.01
ND
u - Concentration is below the detection limit
d - Concentration determined using a
dilution factor
2 of 7
-------
1998 UATMP CARBONYLS
Sample Site: El Paso, TX
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15404 D2
2/11/99
3/16/99
09CO065
ppbv
1.28
0.50
ND
0.49
0.07
0.05
0.03
0.02
ND
0.02
0.02
0.01
ND
15404R2
2/11/99
3/16/99
09CO066
ppbv
1.28
0.50
ND
0.49
0.08
0.05
0.03
0.03
ND
0.03
0.02
0.01
ND
15434
2/17/99
3/16/99
09CO036
ppbv
6.41d
2.57
ND
2.52
0.24
0.10
0.12
0.15
ND
ND
0.09
0.14
ND
15466
2/23/99
3/16/99
09CO046
ppbv
6.01
2.38
0.02
1.97
0.23
0.14
0.11
0.14
ND
0.15
0.08
0.13
ND
15456
3/1/99
3/17/99
O9CQ010
ppbv
2.94
0.86
0.01
1.11
0.13
0.06
0.05
0.04
ND
0.02
0.04
0.03
ND
15496
3/7/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15528
3/13/99
3/31/99
O9C%023
ppbv
2.55
0.96
ND
1.40
0.15
0.06
0.06
0.05
ND
0.02
0.04
0.02
ND
15526
3/19/99
4/1/99
O9C%028
ppbv
3.04
1.13
0.02
1.40
0.18
0.07
0.07
0.05
ND
0.02
0.04
0.03
0.01
u - Concentration is below the detection limit
d - Concentration determined using a
dilution factor
3 of 7
-------
1998 UATMP CARBONYLS
Sample Site: El Paso, TX
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15617
3/^1^99 ;
5/12/99
69Ek620
ppbv
2.57
0.70
ND
0.95
0.08
0.03
0.05
0.04
ND
0.02
0.01
0.02
ND
15635
4/6/99
5/12/99
O9EK028
ppbv
5.80
2.78
0.02
2.45
0.28
0.09
0.15
0.16
ND
0.07
0.07
0.12
0.01
15669D1
4/12/99
5/20/99
O9ES029
ppbv
4.13
1.74
ND
1.95
0.31
0.10
0.13
0.10
ND
0.05
0.05
0.04
0.01
15669R1
4/12/99
5/20/99
O9ES030
ppbv
4.13
1.76
ND
1.97
0.31
0.11
0.13
0.09
ND
0.05
0.06
0.04
0.01
15671 D2
4/12/99
5/20/99
O9ES031
ppbv
3.72
1.51
ND
1.62
0.27
0.08
0.11
0.09
ND
0.05
,.0.06
0.04
0.01
15671 R2
4/12/99
5/20/99
O9ES032
ppbv
3.71
1.49
ND
1.60
0.28
0.08
0.11
0.08
ND
0.05
0.06
0.04
0.01
15689
4/18/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15703
4/24/99
5/20/99
O9ES023
ppbv
2.23
0.88
ND
0.92
0.15
0.03
0.07
0.04
ND
0.03
0.01
0.03
ND
u - Concentration is below the detection limit
d - Concentration determined using a
dilution factor
4 of 7
-------
1998 UATMP CARBONYLS
Sample Site: El Paso, TX
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15724D1
5/6/99
6/5/99
Q9FD033
ppbv
2.51
0.72
0.01
1.04
0.12
ND
0.21
0.06
0.03
0.03
0.04
0.02
ND
15724R1
5/6/99
6/5/99
Q9FD034
ppbv
2.63
0.74
0.01
1.09
0.09
ND
0.19
0.06
0.02
0.03
0.04
0.07
ND
15726 D2
5/6/99
6/5/99
Q9FD035
ppbv
2.45
0.68
0.01
0.95
0.10
ND
0.18
0.06
0.04
0.03
0.05
0.01
ND
15726 R2
5/6/99
6/5/99
Q9FD036
ppbv
2.47
0.64
0.01
0.92
0.08
ND
0.18
0.04
0.02
0.02
0.04
0.02
ND
15782
5/18/99
6/9/99
Q9FH020
ppbv
3.57
1.19
ND
1.27
0.15
0.02
0.27
0.05
0.03
0.04
0.05
0.02
ND
15814
5/30/99
6/10/99
Q9FH029
ppbv
3.58
1.03
0.01
1.34
0.11
ND
0.20
0.05
0.04
0.04
0.06
0.03
ND
15845
6/11/99
6/19/99
O9FR024
ppbv
3.14
0.82
0.02
1.06
0.10
0.01
0.09
0.07
0.01
0.04
0.07
0.06
ND
15934
6/23/99
7/7/99
O9GF023
ppbv
3.90
1.39
0.02
1.93
0.19
0.01
0.17
0.08
0.01
0.05
0.07
0.04
ND
u - Concentration is below the detection limit
d - Concentration determined using a
dilution factor
5 of 7
-------
1998 UATMP CARBONYLS
Sample Site: El Paso, TX
Derivatized Gone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15979
7/5/99
8/6/99
O9HE017
ppbv
21.09d
6.68d
0.51d
0.51d
0.29d
O.OSd
0.27d
0.63d
ND
0.20d
0.23d
0.27d
O.OSd
16129
7/17/99
8/6/99
O9HE030
ppbv
30.14d
6.79
0.75
0.22
0.30
0.06
0.21
0.65
ND
0.33
0.17
0.24
ND
16197
7/29/99
8/6/99
O9HE038
ppbv
29.15d
6.75
0.66
0.38
0.25
0.06
0.20
0.63
ND
0.24
0.16
0.26
ND
16329
8/10/99
8/25/99
O9HX019
ppbv
7.20
2.47
0.18
0.84
0.11
0.01
0.17
0.17
0.01
0.07
0.09
0.07
ND
16445
8/22/99
9/11/99
O9IJ024
ppbv
9.44d
3.04
0.12
1.77
0.28
0.01
0.34
0.18
0.020
0.09
0.10
0.10
ND
16687
9/3/99
9/23/99
O9IV018
ppbv
6.95
2.01
0.12
1.37
0.16
0.01
0.18
0.14
ND
0.05
0.08
0.06
ND
u - Concentration is below the detection limit
d - Concentration determined using a
dilution factor
6 of 7
-------
FIELD BLANK DATA
Sample site: El Paso, TX
RAW AMOUNT
Derivatized Cone. (ug/mL)
Data File ID
FBID
Sample date
Date Analyzed
Q8KK01 1
15002FB
9/20/98
11/11/98
09C$010
15529FB
3/13/99
3/30/99
O9EK008
15636FB
4/6/99
5/11/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.09
0.36
0.00
0.44
0.00
0.00
0.45
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.03
0.00
0.00
0.00
0.00
0.07
0.00
0.00
0.00
0.00
0.06
0.08
0.00
0.33
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
O9ES008
15704FB
4/24/99
5/19/99
0.08
0.08
0.05
0.15
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
Q9FH010
15783FB
5/18/99
6/9/99
0.42
0.09
0.00
0.23
0.00
0.00
0.38
0.00
0.00
0.00
0.00
0.04
0.00
Field Blanks
Underivatized Conc.(total ug)
Data File ID
FBID
Date Analyzed
Q8KK01 1
15002FB
11/11/98
O9C$010
15529FB
3/30/99
O9EK008
15636FB
5/11/99
O9ES008
15704FB
5/19/99
Q9FH010
15783 FB
6/9/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.05
0.28
ND
0.42
ND
ND
0.51
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.02
ND
ND
ND
ND
0.10
ND
ND
ND
ND
0.04
0.06
ND
0.32
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.05
0.07
0.05
0.15
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.24
0.07
ND
0.22
ND
ND
0.44
ND
ND
ND
ND
0.05
ND
7 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Garyville, LA
GALA
Derivatized Cone. (ug/rnL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
14801
9/2/98
10/28/98
Q8J-018
ppbv
1.69
0.59
0.04
0.48
0.11
ND
0.17
0.09
0.02
0.05
0.02
0.05
0.01
14805
9/14/98
10/30/98
Q8J#021
ppbv
1.84
1.39
0.03
0.25
0.18
ND
0.33
0.04
0.01
0.22
ND
0.08
ND
15099
9/26/98
11/12/98
Q8KK035
ppbv
2.15
1.00
0.04
0.31
0.23
ND
0.40
0.07
0.03
0.24
0.04
0.09
ND
15117
10/8/98
11/16/98
Q8KP019
ppbv
2.15
1.11
0.02
0.69
0.23
ND
0.42
0.07
0.03
0.31
0.02
0.09
ND
15134
10/14/98
11/16/98
Q8KP020
ppbv
3.26
1.39
0.02
0.79
0.27
ND
0.45
0.06
0.03
0.23
0.04
0.09
ND
15172
10/28/98
11/25/98
Q8KW020
ppbv
2.26
1.33
0.03
0.42
0.27
ND
0.48
0.08
0.06
0.27
0.03
0.10
ND
15182
11/7/98
12/22/98
Q8LU022
ppbv
1.71
1.30
0.02
0.86
0.22
ND
0.27
0.08
0.044
0.23
0.04
0.12
ND
15232
11/19/98
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15265
12/1/98
1/8/99
O9AG027
ppbv
1.80
1.36
0.01
0.62
0.25
0.01
0.19
0.04
0.01
0.18
0.03
0.10
ND
u - Concentration is below the detection limit
1 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Garyville, LA
Derivatized Cone. (ug/mL) ;
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15257
12/13/98
1/8/99
O9AG030
ppbv
0.88
0.63
0.01
0.65
0.15
0.005
0.14
0.03
0.01
0.15
0.02
0.07
ND
15295
12/25/98
1/8/99
O9AG041
ppbv
0.58
0.50
0.02
0.51
0.11
0.005
0.11
0.03
0.01
0.12
0.02
0.07
0.003
15398D1
2/5/99
3/16/99
09CO072
ppbv
2.64
1.29
ND
0.50
0.34
0.07
0.18
0.05
0.04
0.29
0.03
0.13
ND
15398R1
2/5/99
3/16/99
09CO073
ppbv
2.63
1.29
ND
0.46
0.32
0.07
0.18
0.05
0.04
0.30
0.03
0.14
ND
15396 D2
2/5/99
3/16/99
09CO074
ppbv
2.40
1.22
ND
0.62
0.32
0.07
0.16
0.05
0.04
0.27
0.03
0.11
ND
15396 R2
2/5/99
3/17/99
09CO075
ppbv
2.40
1.22
ND
0.59
0.30
0.08
0.17
0.06
0.040
0.27
0.03
0.11
ND
15412
2/17/99
3/16/99
09CO037
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15460
2/23/99
3/16/99
09CO047
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
u - Concentration is below the detection limit
2jaf7
-------
1998 UATMP CARBONYLS
Sample Site: Garyville, LA
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSJSDATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15505
3/7/99
3/17/99
O9CQ011
ppbv
2.24
1.24
ND
0.76
0.31
0.04
0.21
0.05
0.05
0.37
0.05
0.11
ND
15524
3/13/99
4/1/99
O9C%024
ppbv
1.55
0.70
ND
0.31
0.22
0.02
0.11
0.02
0.04
0.24
0.01
0.07
ND
15561
3/19/99
4/14/99
09DM023
ppbv
2.95
1.21
ND
0.52
0.26
ND
0.12
0.03
ND
0.15
0.02
0.08
ND
15592D1
3/25/99
4/14/99
09DM049
ppbv
1.34
0.50
ND
0.51
0.15
ND
0.06
0.02
ND
0.09
0.01
0.04
ND
15592 R1
3/25/99
4/14/99
O9DM050
ppbv
1.35
0.50
ND
0.52
0.15
ND
0.06
0.02
ND
0.09
0.01
0.05
ND
15594 D2
3/25/99
4/14/99
O9DM051
ppbv
1.69
0.63
ND
0.48
0.16
ND
0.07
0.02
ND
0.11
0.01
0.07
ND
15594R2
3/25/99
4/14/99
O9DM052
ppbv
1.73
0.64
ND
0.48
0.15
ND
0.07
0.02
ND
0.11
0.01
0.07
ND
15621
3/31/99
5/12/99
O9EK021
ppbv
1.67
0.93
0.01
0.35
0.14
0.03
0.09
0.03 •
ND
0.08
0.001
0.05
ND
u - Concentration is below the detection limit
3 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Garyville, LA
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15663D1
4/12/99
5/20/99
O9ES033
ppbv
3.66
0.99
ND
1.04
0.23
0.12
0.11
0.03
ND
0.11
ND
0.06
ND
15663 R1
4/12/99
5/20/99
O9ES034
ppbv
3.67
1:00
ND
1.04
0.17
0.04
0.11
0.03
ND
0.14
ND
0.06
ND
15665D2
4/12/99
5/20/99
O9ES035
ppbv
3.59
0.98
ND
0.64
0.22
0.04
0.10
0.03
ND
0.11
0.00
0.06
ND
15665 R2
4/12/99
5/20/99
O9ES036
ppbv
3.69
0.98
ND
0.64
0.22
0.04
0.10
0.03
ND
0.14
ND
0.06
ND
15691
4/18/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15693 D1
4/24/99
6/5/99
Q9FD029
ppbv
2.38
0.80
0.02
0.47
0.19
ND
ND
0.12
ND
0.12
0.10
ND
ND
15693 R1
4/24/99
6/5/99
Q9FD030
ppbv
2.48
0.81
0.03
0.49
0.21
ND
ND
0.12
ND
0.12
0.05
ND
ND
15694D2
4/24/99
6/5/99
Q9FD031
ppbv
2.26
0.80
0.02
0.32
0.19
ND
ND
0.11
ND
0.10
0.05
ND
ND
u - Concentration is below the detection limit
4 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Garyville, LA
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15694R2
4/24/99
6/5/99
Q9FD032
ppbv
2.22
0.76
0.01
0.32
0.19
ND
ND
0.12
ND
0.10
0.05
ND
ND
15741
4/30/99
6/5/99
Q9FD019
ppbv
3.25
1.00
0.01
0.96
0.24
ND
ND
0.09
ND
0.20
0.04
ND
ND
15753
5/6/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15755
5/6/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15777
5/12/99
6/9/99
Q9FH017
ppbv
2.10
0.80
0.02
0.32
0.17
' ND
0.38
0.08
0.055
0.07
0.05
0.04
ND
15767D1
5/18/99
6/10/99
Q9FH040
ppbv
4.54
1.21
0.04
0.80
0.24
ND
0.52
0.12
0.038
0.16
0.07
0.08
ND
15767R1
5/18/99
6/10/99
Q9FH041
ppbv
4.56
1.25
0.04
0.82
0.23
ND
0.47
0.05
0.075
0.12
0.06
0.08
ND
15768 D2
5/18/99
6/10/99
Q9FH042
ppbv
4.76
1.23
0.04
0.48
0.26
ND
0.44
0.10
0.035
0.16
0.05
0.08
ND
u - Concentration is below the detection limit
5 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Garyville, LA
Deri vatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
hlexaldenyde
2,5-Dimethylbenzaldehyde
15768R2
5/18/99
6/10/99
Q9FH043
ppbv
4.65
1.25
0.02
0.46
0.25
ND
0.40
0.10
0.086
0.17
0.03
0.06
ND
15818
5/30/99
6/10/99
Q9FH030
ppbv
2.21
1.17
0.04
0.38
0.33
0.12.
0.42
0.07
0.026
0.16
0.07
0.07
0.01
15857
6/11/99
6/18/99
O9FR019
ppbv
2.18
1.06
ND
0.42
0.27
ND
0.25
0.12
0.02
0.21
0.05
0.10
ND
15986
7/5/99
8/6/99
O9HE018
ppbv
1.91
0.77
ND
0.29
0.25
ND
0.19
0.06
0.02
0.23
0.05
0.13
ND
16058
7/17/99
8/6/99
O9HE040
ppbv
3.22
1.93
ND
0.29
0.29
ND
0.23
0.10
0.02
0.21
0.05
0.14
ND
16206
7/29/99
8/6/99
O9HE039
ppbv
4.57
1.71
ND
0.38
0.44
ND
0.31
0.18
0.02
0.34
0.07
0.18
ND
16350
8/10/99
8/25/99
O9HX020
ppbv
2.37
1.26
ND
0.49
0.38
ND
0.30
0.09
0.02
0.30
0.07
0.15
ND
16684
9/3/99
9/23/99
O9IV017
ppbv
1.84
1.03
ND
0.31
0.34
ND
0.19
0.06
ND
0.22
0.03
0.16
ND
u - Concentration is below the detection limit
6 of 7
-------
FIELD BLANK DATA
Sample site: Garyville, LA
RAW AMOUNT
Derivatized Cone. (ug/mL)
Data File ID
FBID
Sample date
Date Analyzed
Q8KK013
15100FB
9/26/98
11/11/98
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.04
0.31
0.00
0.45
0.02
0.00
0.51
0.04
0.00
0.02
0.00
0.04
0.00
Field Blanks
Underivatized Cone, (total ug)
Data File ID
FBID
Date Analyzed
Q8KK013
15100FB
11/11/98
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.02
0.24
ND
0.44
0.02
ND
0.58
0.06
ND
0.03
ND
0.06
ND
7 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Hahnville, LA
HALA
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15105
9/14/98
10/30/98
Q8J#022
ppbv
1.05
0.30
0.01
0.18
0.05
ND
0.10
0.02
0.03
0.03
ND
0.06
ND
15102
9/26/98
11/12/98
Q8KK036
ppbv
1.97
0.41
0.02
0.17
0.10
ND
0.25
0.03
0.04
0.04
ND
0.06
ND
15132
10/14/98
11/17/98
Q8KP022
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15170
10/26/98
11/25/98
Q8KW017
ppbv
4.04
1.04
0.03
1.37
0.14
ND
0.40
0.06
0.08
0.05
0.03
0.07
ND
15180
11/7/98
12/22/98
Q8LU024
ppbv
2.09
1.12
0.04
1.27
0.15
ND
0.24
0.05
0.06
0.05
0.06
0.05
ND
15224
11/19/98
12/22/98
Q8LU031
ppbv
5.04
1.38
0.19
0.77
0.25
ND
0.20
0.04
0.12
0.06
0.06
0.06
0.02
15222
12/1/98
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15255
12/13/98
1/8/99
O9AG032
ppbv
0.83
0.48
0.02
0.90
0.06
0.003
0.16
0.02
0.002
0.04
0.02
0.03
0.002
u - Concentration is below the detection limit
1 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Hahnville, LA
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15293
12/25/98
1/8/99
O9AG043
ppbv
0.74
0.37
0.01
0.70
0.06
0.004
0.29
0.02
0.01
0.04
0.02
0.03
ND
15315
1/9/99
2/20/99
O9BS021
ppbv
1.03
0.67
0.005
1.02
0.11
0.01
0.15
0.02
ND
0.14
0.01
0.04
ND
15392D1
2/5/99
3/16/99
09CO068
ppbv
2.71
1.12
ND
0.88
0.32
0.13
0.11
0.06
0.02
0.23
0.02
0.06
ND
15392R1
2/5/99
3/16/99
09CO069
ppbv
2.68
1.10
ND
0.86
0.31
0.13
0.11
0.08
0.03
0.26
0.03
0.07
ND
15394 D2
"2/5/99
3/16/99
09CO070
ppbv
2.59
1.08
ND
0.83
0.31
0.12
0.11
0.08
ND
0.25
. 0.03
0.06
ND
15394R2
2/5/99
3/16/99
09CO071
ppbv
2.56
1.03
ND
0.83
0.31
0.11
0.10
0.06
ND
0.24
0.03
0.07
ND
15416
2/13/99
VOID
09CO050
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15458
2/23/99
3/16/99
09CO050
ppbv
1.43
0.80
ND
1.13
0.20
0.06
0.10
0.04
0.03
0.21
0.05
0.05
ND
u - Concentration is below the detection limit
2 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Hahnville, LA
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15494
3/1/99
3/17/99
O9CQ014
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15492
3/7/99
3/17/99
O9CQ016
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15557D1
3/19/99
6/5/99
Q9FD042
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15559 D2
3/19/99
6/5/99
Q9FD044
ppbv
3.10
1.44
0.02
1.43
0.19
ND
0.58
0.06
ND
0.14
0.04
0.08
ND
15596
3/25/99
4/14/99
O9DM029
ppbv
0.03
0.04
ND
0.09
0.01
ND
0.01
ND
ND
ND
0.003
ND
ND
15619
3/31/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15681
4/6/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15659D1
4/18/99
5/20/99
O9ES042
ppbv
1.49
1.05
ND
1.19
0.19
0.07
0.07
0.02
ND
0.05
0.01
0.06
0.00
u - Concentration is below the detection limit
3nf7
-------
1998 UATMP CARBONYLS
Sample Site: Hahnville, LA
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaieraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15659R1
4/18/99
5/20/99
09ES043
ppbv
1.50
1.04
ND
1.19
0.19
0.07
0.08
0.02
ND
0.04
0.00
0.05
ND
15661 D2
4/18/99
5/20/99
O9ES044
ppbv
1.75
1.13
ND
1.27
0.20
0.07
0.08
0.02
ND
0.05
0.01
0.06
ND
15661 R2
4/18/99
5/20/99
O9ES045
ppbv
1.74
1.12
ND
1.26
0.20
0.08
0.08
0.02
ND
0.05
0.01
0.06
ND
15738 D1
4/30/99
6/5/99
Q9FD038
ppbv
1.70
0.54
0.01
1.22
0.06
ND
ND
ND
ND
ND
0.04
0.02
ND
15738R1
4/30/99
6/5/99
Q9FD039
ppbv
1.68
0.52
0.01
1.20
0.06
ND
ND
ND
ND
ND
0.03
0.02
ND
15739D2
4/30/99
6/5/99
Q9FD040
ppbv
1.92
0.55
0.01
1.17
0.06
ND
ND
ND
ND
0.03
0.04
0.02
ND
15739R2
4/30/99
6/5/99
Q9FD041
ppbv
1.85
0.55
0.01
1.13
0.05
ND
ND
ND
ND
0.02
0.02
0.02
ND
15763
5/6/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
u - Concentration is below the detection limit
4 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Hahnville, LA
Derivatized Cone. (ug/mL)
£A^JPL|t>ATE '•''^••'f- V-v:;:.. -.•>•" '
ANALYSIS DATE
FILENAME :
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15765
5/6/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15770
5/18/99
6/9/99
Q9FH021
ppbv
2.99
1.33
0.05
0.49
0.18
ND
0.16
0.06
0.03
0.09
0.04
0.06
ND
15820 D1
5/30/99
6/11/99
Q9FK004
ppbv
1.24
0.53
0.01
0.29
0.09
ND
0.23
0.05
0.03
0.03
ND
0.04
ND
15820R1
5/30/99
6/11/99
Q9FK005
ppbv
1.29
0.55
0.02
0.28
0.08
ND
0.23
0.04
ND
0.03
ND
0.04
ND
15821 D2
5/30/99
6/11/99
Q9FK006
ppbv
1.34
0.60
0.02
0.28
0.10
ND
0.23
0.03
0.02
0.02
0.03
0.04
ND
15821 R2
5/30/99
6/11/99
Q9FK007
ppbv
1.35
0.58
0.01
0.28
0.09
ND
0.25
0.03
0.03
0.03
0.03
0.04
ND
15855
6/11/99
6/18/99
O9FR020
ppbv
1.33
0.56
ND
0.48
0.12
ND
0.10
0.06
0.01
0.05
0.03
0.07
ND
15984
7/5/99
8/6/99
O9HE019
ppbv
1.17
0.38
ND
0.03
0.06
ND
0.05
0.03
0.01
0.02
0.01
0.04
ND
u - Concentration is below the detection limit
-------
1998 UATMP CARBONYLS
Sample Site: Hahnville, LA
Deri vati7ed Gone. (ug/mL)
SAMPLE'DAfE;:.:"/::-'-"' ':::;-:;.':: • • '•
ANALYSIS dA?E
RLE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
16061
7/1 If/99
8/6/99 •'"..
d9HE031
ppbv
1.01
0.40
0.00
0.03
0.05
ND
ND
0.01
ND
0.03
ND
0.04
ND
162Q2
7^9/99
VOID
vdib
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
16348
;8/io/99
8/25/99
O9HX621
ppbv
0.93
0.17
ND
0.06
0.04
ND
ND
0.02
0.01
0.03
0.02
0.03
ND
1644?
\'.?$£ii9'l
9/^/99
69^625
ppbv
1.02
0.36
0.01
0.04
0.05
ND
0.17
0.02
0.01
0.03
0.01
0.02
ND
16678
: 9/3/99
i 9/23/99
G)9iV6l6
ppbv
0.61
0.33
0.01
0.04
0.03
ND
0.03
0.01
0.01
0.01
ND
0.03
ND
u - Concentration is below the detection limit
6 Of 7
-------
FIELD BLANK DATA
Sample site: Hahnville, LA
RAW AMOUNT
Derivatized Cone. (ug/mL)
Data File ID
FBID
Sample date
Date Analyzed
Q8KK014
15103FB
9/26/98
11/11/98
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.11
0.17
0.03
0.44
0.00
0.00
0.68
0.00
0.00
0.04
0.00
0.05
0.00
Field Blanks
Underivatized Cone.(total ug)
Data File ID
FBID
Date Analyzed
Q8KK014
15103FB
11/11/98
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.06
0.14
0.02
0.43
ND
ND
0.77
ND
ND
0.05
ND
0.07
ND
7 of 7
-------
1998 UATMP CARBONYLS
Sample Site: N. Little Rock, AK
PARR
Derivatized Cone. (ug/mL) :
SAMPLE DATE ' : ' :- ' - : :' : ;:i '.>;
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
14683
9ti/&
10/28^98
QBJ^bii
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
14699
9/8/98
10/28/98
Q8J-026
ppbv
5.04
1.22
0.04
1.85
0.12
ND
0.43
0.21
0.02
0.02
0.12
0.04
ND
14966
9/20/98
11/12/98
Q8KK041
ppbv
1.94
0.75
0.10
0.51
0.11
ND
0.14
0.04
0.03
0.06
0.05
0.07
0.03
15125
10/14/98
11/17/98
Q8KP023
ppbv
2.74
1.14
0.04
2.18
0.15
ND
0.64
0.09
0.01
0.05
0.04
0.03
ND
15146
10/26/98
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15186
11/7/98
12/22/98
Q8LU025
ppbv
1.51
1.02
0.02
1.57
0.09
ND
0.20
0.05
0.04
0.03
0.04
0.01
ND
15210
11/19/98
12/22/98
Q8LU032
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15242
12/1/98
12/22/98
Q8LU039
ppbv
1.20
0.65
0.02
1.20
0.06
ND
0.21
0.04
0.04
0.03
0.03
0.02
ND
u - Concentration is below the detection limit
1 of 4
-------
1998 UATMP CARBONYLS
Sample Site: N. Little Rock, AK
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
folualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15261
12/13/98
1/8/99 ;
O9AG033
ppbv
0.75
0.47
0.01
0.83
0.06
ND
0.10
0.02
0.01
0.01
0.01
0.02
ND
15279
:i;2/25V98
1/8/99
O9AG044
ppbv
1.60
1.24
0.04
1.00
0.12
0.01
0.13
0.04
0.01
0.02
0.02
0.04
ND
15325
1/6/99
2/26/99
O9BS024
ppbv
2.34
1.19
0.02
1.58
0.13
0.01
0.14
0.04
0.01
0.03
0.03
0.04
ND
15363;
1/^8/99
2/20/99
O9BS025
ppbv
1.26
0.70
0.02
1.25
0.10
0.004
0.09
0.04
0.01
0.03
0.03
0.03
ND
15373
1/3d/99
3/16/99
09C6025
ppbv
1.26
0.49
ND
0.78
0.08
ND
0.04
0.04
ND
ND
0.03
0.02
ND
15400
2/11/99
3/16/99
09CO030
ppbv
1.01
0.43
ND
0.46
0.08
0.03
0.03
0.02
ND
ND
0.03
0.03
ND
15432
2/17/99
3/16/99
09CO041
ppbv
1.36
0.62
ND
1.28
0.11
0.08
0.04
0.05
ND
0.03
0.04
0.04
ND
15462
2/23/99
3/16/99
09CO048
ppbv
1.83
0.79
ND
1.38
0.14
0.09
0.05
0.05
ND
0.04
0.04
0.02
ND
u - Concentration is below the detection limit
2 o* 4
-------
1998 UATMP CARBONYLS
Sample Site: N. Little Rock, AK
Derivatized Cone. (ug/mL) ; :
PiMi>LEbAtE
ANALYSIS PATE
PiLENAIVIE
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15514
3/-I/99 ;:
3/17^9
osiCiadis
ppbv
2.99
1.34
ND
2.02
0.24
0.14
0.09
0.07
ND
0.06
0.05
0.05
ND
15506
:':; 3/7/$$ :;
3/17/99 ;
d9dd6i7
ppbvi
1.09
0.52
ND
0.87
0.09
0.04
0.05
0.01
ND
ND
0.02
0.02
ND
15598 O1
^3/1^/99
: 4/1 4/99
O9DM035
ppbv
1.55
0.68
ND
1.25
0.11
ND
0.04
0.03
ND
0.02
0.02
0.03
ND
15598 Rt
3/17/99 !'••:
4714/99
O9tii\/ld37
ppbv
1.57
0.68
ND
1.26
0.11
ND
0.04
0.03
ND
0.01
0.02
0.02
ND
1560QP2
:;3/i7/99:::
i4/14/99
ib9t)ivid38
ppbv
1.54
0.67
ND
1.25
0.11
ND
0.04
0.03
ND
0.02
0.02
0.02
ND
15600 RZ
3/177991
4/14/99
dgbMdM
ppbv
1.59
0.67
ND
1.26
0.11
ND
0.04
0.03
ND
0.02
0.02
0.02
ND
15585:
:3/25/99 : i
4/14799: ;;
b9C>n/H)28
ppbv
1.39
0.69
ND
1.28
0.12
ND
0.05
0.02
ND
0.02
0.01
0.03
ND
15615
3/31/99
5/12/99 ;=
O9Ekd23
ppbv
1.50
0.70
ND
0.82
0.12
0.06
0.06
0.04
ND
0.02
0.00
0.03
ND
u - Concentration is below the detection limit
3 of 4
-------
FIELD BLANK DATA
Sample site: N. Little Rock, AR
RAW AMOUNT
Derivatized Cone. (ug/mL)
Data File ID
FBID
Sample date
Date Analyzed
Q8KK012
14967FB
9/21/98
11/11/98
O9DM010
15586FB
3/25/99
4/13/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.10
0.07
0.00
0.37
0.00
0.00
~0.61
0.00
0.00
0.00
0.00
0.03
0.00
0.14
0.06
0.00
0.13
0.02
0.00
0.00
0.00
0.00
0.00
0.02
0.00
0.00
Field Blanks
Underivatized Conc.(tota! ug)
Data File ID
FBID
Date Analyzed
Q8KK012
14967FB
11/11/98
O9DM010
15586FB
4/13/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.06
0.06
ND
0.36
ND
ND
0.70.
ND
ND
ND
ND
0.05
ND
0.08
0.05
ND
0.12
0.02
ND
ND
ND
ND
ND
0.03
ND
ND
4 of 4
-------
1998 UATMP CARBONYLS
Sample Site: Rutland, VT
RUVT
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
B uty r/lsobuty ra Idehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
14691
9/2/98
10/28/98
Q8J-020
ppbv
2.18
0.93
0.04
ND
1.36
ND
0.39
0.06
0.01
0.03
ND
0.04
ND
14822
9/14/98
10/30/98
Q8J#023
ppbv
1.47
0.86
0.14
0.83
0.11
ND
0.11
0.06
0.02
0.03
0.03
0.05
ND
15061
9/26/98
11/12/98
Q8KK042
ppbv
1.70
1.07
0.15
1.18
0.15
ND
0.15
0.05
0.03
0.05
0.04
0.06
0.02
15112
10/8/98
11/17/98
Q8KP024
ppbv
1.53
1.06
0.05
1.04
0.14
ND
0.44
0.05
0.03
0.04
0.04
0.03
ND
15136
10/20/98
11/17/98
Q8KP025
ppbv
1.60
0.77
0.01
1.46
0.08
ND
0.41
0.03
ND
0.02
ND
0.02
ND
15158
11/1/98
11/25/98
Q8KW023
ppbv
1.13
0.63
0.02
0.94
0.06
ND
0.33
0.03
ND
0.02
ND
0.01
ND
15202
11/13/98
11/25/98
Q8KW028
ppbv
1.75
0.83
0.03
1.27
0.09
ND
0.21
0.05
0.020
0.02
0.04
0.02
0.01
15230
11/25/98
12/21/98
Q8LU012
ppbv
1.44
0.77
0.02
1.00
0.07
ND
0.16
0.05
0.02
0.02
0.03
0.02
0.02
u - Concentration is below the detection limit
1 of 6
-------
1998 UATMP CARBONYLS
Sample Site: Rutland, VT
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15246
12/7/98
12/22/98
Q8LU017
ppbv
1.36
0.62
0.01
0.99
0.07
ND
0.12
0.03
ND
0.02
0.03
0.02
0.01
15281
12/19/98
1/8/99
O9AG036
ppbv
2.13
1.47
0.07
1.35
0.17
0.02
0.19
0.09
0.02
0.03
0.08
0.04
ND
15307
12/31/98
2/20/99
O9BS018
ppbv
2.02
1.29
0.06
1.08
0.13
0.02
0.14
0.08
0.01
0.03
0.07
0.03
ND
15321
1/12/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15346 D1
1/24/99
2/20/99
O9BS035
ppbv
1.08
0.80
0.01
0.96
0.09
0.01
0.08
0.05
0.01
0.02
0.04
0.05
ND
15346 R1
1/24/99
2/20/99
O9BS036
ppbv
1.11
0.80
0.01
0.95
0.08
0.01
0.08
0.05
0.01
0.02
0.04
0.05
0.00
15348D2
1/24/99
2/20/99
O9BS038
ppbv
1.11
0.80
0.01
0.94
0.09
0.01
0.08
0.05
0.01
0.02
0.04
0.04
ND
15348R2
1/24/99
2/20/99
O9BS039
ppbv
1.13
0.81
0.01
0.96
0.09
0.01
0.09
0.05
0.01
0.02
0.04
0.04
ND
u - Concentration is below the detection limit
2 of 6
-------
1998 UATMP CARBONYLS
Sample Site: Rutland, VT
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15410
2/5/99
3/16/99
09CO027
ppbv
1.10
0.59
ND
0.72
0.10
0.04
0.04
0.02
ND
0.03
0.02
0.01
ND
15446
2/17/99
3/16/99
09CO038
ppbv
1.91
0.98
ND
1.25
0.16
0.10
0.06
0.05
ND
0.03
0.04
0.04
ND
15480
3/1/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15551
3/13/99
4/1/99
O9C%025
ppbv
1.32
0.66
ND
0.76
0.11
0.04
0.04
0.02
ND
0.02
0.01
0.005
ND
15567
3/19/99
4/14/99
O9DM024
ppbv
1.44
0.68
ND
0.65
0.10
ND
0.04
0.01
ND
0.01
0.01
0.01
ND
15629 D1
3/25/99
5/12/99
09EK042
ppbv
1.46
0.58
0.02
0.81
0.09
0.02
0.04
0.01
ND
0.01
ND
0.01
ND
15629 R1
3/25/99
5/12/99
O9EK043
ppbv
1.48
0.58
0.02
0.81
0.09
0.02
0.04
0.01
ND
0.01
ND
0.01
ND
15631 D2
3/25/99
5/12/99
O9EK044
ppbv
1.55
0.58
0.02
0.82
0.09
0.02
0.04
0.02
ND
0.01
0.00
0.01
ND
u - Concentration is below the detection limit
3 of 6
-------
1998 UATMP CARBONYLS
Sample Site: Rutland, VT
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovateraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15631 R2
3/25/99
5/12/99
O9EK045
ppbv
1.59
0.59
0.02
0.82
0.09
0.02
0.04
0.02
ND
0.01
ND
0.01
ND
15633
4/6/99
5/19/99
O9ES013
ppbv
2.19
1.11
ND
1.41
0.17
0.07
0.09
0.05
ND
0.03
0.01
0.03
ND
15679
4/18/99
5/19/99
O9ES018
PPbV
0.64
0.30
ND
0.46
0.05
0.02
0.02
0.01
ND
0.01
ND
0.01
ND
15732
4/30/99
6/5/99
Q9FD020
ppbv
3.20
1.65
0.02
2.23
0.19
ND
0.48
0.08
0.013
0.07
0.06
0.11
ND
15823
5/12/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15825
5/12/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15785
5/24/99
6/10/99
Q9FH025
ppbv
2.25
0.85
0.03
1.22
0.11
ND
0.34
0.06
ND
0.04
0.04
0.03
ND
15905
6/5/99
7/6/99
09GF014
ppbv
3.56
1.50
ND
2.31
0.23
ND
0.33
0.15
0.03
0.06
0.05
0.08
0.01
u - Concentration is below the detection limit
4of 6
-------
1998 UATMP CARBONYLS
Sample Site: Rutland, VT
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15926
6/17/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
16027
6/29/99
8/6/99
O9HE011
ppbv
3.35
1.10
ND
0.20
0.20
ND
0.21
0.09
0.02
0.07
0.05
0.09
0.01
16259
7/17/99
8/19/99
O9HQ028
ppbv
5.11
1.52
0.02
0.49
0.32
0.01
0.24
0.09
0.03
0.10
0.04
0.10
ND
16251
7/23/99
8/19/99
09HQ032
ppbv
4.44
1.57
0.02
1.49
0.26
ND
0.24
ND
0.03
0.08
0.05
0.07
ND
16276
8/4/99
8/25/99
O9HX024
ppbv
2.67
0.96
ND
1.00
0.17
ND
0.24
0.07
0.03
0.06
0.05
0.05
0.01
16488
8/16/99
9/11/99
O9IJ018
ppbv
2.35
1.04
ND
1.31
0.15
ND
0.17
0.05
0.02
0.05
0.05
0.06
0.01
16610
8/28/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
16808
9/9/99
10/1/99
O9I$035
PPby
2.63
1.06
ND
1.57
0.15
ND
0.15
0.11
0.03
0.05
0.05
0.09
ND
u - Concentration is below the detection limit
5 of 6
-------
FIELD BLANK DATA
Sample site: Rutland, VT
RAW AMOUNT
Derivatized Cone. (ug/mL)
Data File ID
FBID
Sample date
Date Analyzed
Q8J#009
14823FB
9/14/98
10/29/98
09C%01 1
15552FB
3/13/99
3/30/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.03
0.05
0.00
0.35
0.00
0.00
0.37
0.00
0.00
0.00
0.00
0.00
0.00
0.05
0.08
0.00
0.16
0.00
0.00
0.00
0.00
0.00
0.00
0.02
0.00
0.00
Field Blanks
Underivatized Conc.(total ug)
Data File ID
FBID
Date Analyzed
Q8J#009
14823FB
10/29/98
O9C%01 1
15552FB
3/30/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.02
0.04
ND
0.34
ND
ND
0.43
ND
ND
ND
ND
ND
ND
0.03
0.06
ND
0.16
ND
ND
ND
ND
ND
ND
0.04
ND
ND
6 of 6
-------
1998 UATMP CARBONYLS
Sample Site: Texarkana, AK
GREY
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
14557
9/1/98
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
14696
9/5/98
10/28/98
Q8J-027
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
14887
9/17/98
10/30/98
Q8J#028
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15119
10/14/98
11/17/98
Q8KP021
ppbv
4.18
1.21
0.03
1.16
0.10
ND
0.41
0.06
0.01
0.07
0.04
0.15
ND
15142
10/25/98
11/25/98
Q8KW013
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
:VOID
VOID
VOID
VOID
• VOID
VOID
15174
11/7/98
12/22/98
Q8LU023
ppbv
1.49
0.82
0.01
0.89
0.08
ND
0.14
0.03
0.02
0.02
0.03
0.02
ND
15220
11/13/98
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15240
12/3/98
12/22/98
Q8LU038
ppbv
1.93
0.39
0.03
1.35
0.04
ND
0.21
0.04
0.03
0.01
0.05
0.03
ND
u - Concentration is below the detection limit
d - Concentration determined using a
dilution factor
Of4
-------
1998 UATMP CARBONYLS
Sample Site: Texarkana, AK
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15259
12/13/98
1/8/99
O9AG031
ppbv
0.50
0.31
0.002U
0.86
0.03
ND
0.11
0.05
ND
0.02
0.03
0.07
ND
15287
12/25/98
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15313
1/6/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15365
1/18/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15371
1/30/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15420
2/11/99
3/16/99
09CO031
ppbv
2.24
0.99
ND
0.55
ND
0.07
0.05
0.05
ND
0.05
0.03
0.04
ND
15440
2/23/99
3/16/99
09CO044
ppbv
1.11
0.63
ND
1.26
0.09
0.04
0.03
0.02
ND
0.03
0.02
0.03
ND
15488
3/7/99
3/17/99
09CQ012
ppbv
2.04
0.91
ND
1.38
0.14
0.05
0.05
0.03
ND
ND
0.03
0.03
ND
u - Concentration is below the detection limit
d - Concentration determined using a
dilution factor
-------
1998 UATMP CARBONYLS
Sample Site: Texarkana, AK
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15508
i3/1 it/99
3/17/99
O90Q013
ppbv
1.37
0.65
ND
0.65
0.10
0.05
0.04
0.03
ND
0.03
0.02
0.03
ND
15531
3/19/99
4/1/99
O9C%029
ppbv
2.02
0.92
ND
1.23
0.22
0.04
0.05
0.03
ND
0.05
0.02
0.03
ND
15565
3/25/99
5/12/99
O9EK018
ppbv
0.38
0.35
0.01
0.41
0.03
0.01
0.02
0.01
ND
0.004
ND
0.01
ND
15623
3/31/99
5/12/99
Q9EK022
ppbv
0.76
0.49
ND
0.74
0.05
0.02
0.03
0.01
ND
0.01
ND
0.02
ND
u - Concentration is below the detection limit
d - Concentration determined using a
dilution factor
3 Of 4
-------
FIELD BLANK DATA
Sample site: GREY
RAW AMOUNT
Derivatized Cone. (ug/mL)
Data File ID
FBID
Sample date
Date Analyzed
Q8J-007
14558FB
9/1/98
10/27/98
Q8J#01 1
14888FB
9/17/98
10/29/98
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
Q8KP007
15097FB
10/6/98
11/16/98
15.46
2.32
0.13
2.36
0.19
0.00
0.96
0.25
0.05
0.39
0.00
1.58
0.12
Field Blanks
Underivatized Conc.(total ug)
Data File ID
FBID
Date Analyzed
Q8J-007
14558FB
10/27/98
Q8J#01 1
14888 FB
10/29/98
Q8KP007
15097FB
11/16/98
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
8.84
1.82
0.12
2.30
0.18
ND
1.10
0.37
0.07
0.51
ND
2.25
0.21
44
-------
1998 UATMP CARBONYLS
Sample Site: Underbill, VT
UNVT
Derivatized Cone.:(ug/mL) :
SAMPLidAW '":;;..' "::'".."'-:". •'"'
ANALYSIS DATE
Fill NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
14681
9/i?M
10/28/98
Q8J~b21
ppbv
0.84
0.32
0.03
0.56
0.04
ND
0.04
0.01
0.01
0.01
ND
0.01
0.01
14816
9/14/98
10/30/98
Q8J#b24
: PPbV
0.57
0.33
0.07
0.55
0.03
ND
0.04
0.02
ND
0.01
ND
0.01
ND
15053
9/26/98
11/12/98
Q8KK043
ppbv
1.06
0.71
0.11
1.07
0.08
ND
0.09
0.04
0.01
0.02
ND
0.02
0.02
15110
10/8/98
11/17/98
Q8KP027
ppbv
0.70
0.50
ND
0.84
0.06
ND
0.48
0.02
ND
0.02
ND
0.02
ND
15140
10/20/98
11/17/98
Q8KP028
ppbv
0.70
0.39
ND
1.14
0.05
ND
0.31
0.02
ND
0.01
ND
0.01
ND
15160
11/1/98
11/25/98
Q8KW024
ppbv
0.52
0.28
0.01
0.72
0.04
ND
0.29
0.03
0.01
0.01
0.02
0.02
ND
15200
11/13/98
11/25/98
Q8KW029
ppbv
0.45
0.30
0.01
0.80
0.03
ND
0.15
0.02
ND
0.01
ND
ND
ND
15226
11/25/98
12/21/98
Q8LU013
ppbv
0.46
0.29
0.01
0.69
0.03
0.01
0.08
0.02
0.01
0.01
0.01
0.01
ND
u - Concentration is below the detection limit
1 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Underbill, VT
Derivatized Gone. (ug/mL)
SAMPLE DAtE
ANALYSIS (DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15248
12/7/98
12/22798
Q8LU018
PpbV :
0.65
0.33
0.01
0.80
0.04
ND
0.08
0.02
0.01
0.01
0.02
0.02
0.01
15289
12/19/98
i/8/99
O9AG038
ppbv
0.63
0.46
0.01
0.70
0.06
0.003
0.08
0.02
ND
0.01
0.01
0.02
0.01
15309
12/31/98
2/20/99
O9BS019
ppbv
0.58
0.39
0.01
0.55
0.04
ND
0.04
0.02
ND
0.01
0.01
0.02
ND
15323
1/12/99
2/20/99
6988023
ppbv
0.87
0.72
0.01
0.90
0.08
0.004
0.08
0.02
ND
0.02
0.01
0.02
ND
15359D1
1/24/99
2/20/99
d9BS040
ppbv
0.51
0.29
0.0007U
0.55
0.04
ND
0.03
0.01
ND
0.01
ND
0.02
ND
15359 R1
1/24/99
2/20/99
69BS041
ppbv Y
0.52
0.29
O.OOOSu
0.54
0.04
ND
0.03
0.01
ND
0.01
ND
0.02
ND
15361 D2
: ji/24/99 :
2/20/99
O9BS042
ppbv
0.54
0.34
0.0006U
0.61
0.04
ND
0.05
0.01
ND
0.01
ND
0.02
ND
15361 R2
1/24/S9
2/20/99
O9BS043
ppbv;
0.56
0.34
O.OOOSu
0.61
0.04
ND
0.04
0.01
ND
0.01
ND
0.02
ND
u - Concentration is below the detection limit
2flf7
-------
1998 UATMP CARBONYLS
Sample Site: Underbill, VT
Derivatized Cone. (ug/mL)
SAJVlP^ifiAti
ANifltLYSI^ DATE
FlL^ NAM1
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15418
2/5/99
3/16/99
09C6d29
ppbv
0.50
0.30
ND
0.59
0.05
0.02
0.02
0.01
ND
ND
0.01
0.01
ND
15448
2/17/99
3/1;67$9
0900640
ppbv
1.20
0.63
ND
0.97
0.10
0.04
0.04
0.02
ND
0.02
0.01
0.01
ND
15486
: 3/1799
3/16>99 :
09CC)053
ppbv
0.87
0.36
ND
0.79
0.07
0.02
0.02
0.01
ND
ND
0.02
ND
ND
15545
3/13/99
4/1/99
O9C%627
ppbv
0.85
0.44
ND
0.67
0.07
0.03
0.02
0.01
ND
0.01
o.oi
0.01
ND
15569 .,:
3/19/99
4/14/99
O9DIM026
ppbv
0.55
0.24
ND
0.49
0.04
ND
0.01
0.003
ND
0.003
0.01
0.01
ND
15581 D1
3/25/69;
•;-: :4/i4/99 :
O9DM053
ppbv
0.45
0.23
ND
0.60
0.04
ND
0.01
0.004
ND
0.002
0.01
0.01
ND
15581 R1
3/25/99 YJ
: 4/1:4/99 :
d9bA/i654
ppbv
0.46
0.23
ND
0.59
0.04
ND
0.01
0.004
ND
ND
0.01
0.01
ND
u - Concentration is below the detection limit
3 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Underbill, VT
Derivatized Cone. (ug/mL)
SAMPLE DATE i
AJNAL.YSIS bATE
F;iLlNAitiEj-;;'.,' ' •:•.;•'
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Folualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15583 02
3/25/99
•:4/14/99
O9DM055
ppbv
0.52
0.26
ND
0.69
0.04
ND
0.01
0.003
ND
0.001
0.01
0.01
ND
15583R2
3/25/99
4/14/90
09DM056
ppbv
0.51
0.26
ND
0.69
0.04
ND
0.01
0.005
ND
0.001
0.01
0.01
ND
15643
4/6/99
1 5/1 9/99
O9ES015
ppbv .;
1.11
0.52
0.02
0.97
0.07
0.03
0.03
0.01
ND
0.01
ND
0.01
ND
15667
4/12/99 :
5/19/99
O9ES019
ppbv
0.78
0.33
ND
0.80
0.04
0.02
0.02
0.01
ND
0.01
ND
0.01
ND
15736 :
4/30/99
6/5/99 ;J
Q9Fd62l
ppbv
1.42
0.63
0.01
1.34
0.06
ND
0.26
0.03
ND
0.03
0.04
0.04
ND
.,1:5.8.0001,
; 5/12/99
6/10/99
d9FHb44
ppbv
1.10
0.49
ND
1.36
0.07
ND
0.26
0.03
0.03
0.02
0.04
0.05
ND
15800R1
5/12/99
6/10/99
Q9FH045
ppbv
1.07
0.52
ND
1.35
0.06
ND
0.25
0.03
0.03
0.02
0.05
0.02
ND
15802 P2
5/12/99
6/11/99:
G9Fk602
ppbv
1.25
0.50
ND
1.39
0.06
ND
0.21
0.07
ND
0.02
0.03
0.03
ND
u - Concentration is below the detection limit
4 a!7
-------
1998 UATMP CARBONYLS
Sample Site: Underbill, VT
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
158Q2R2
5/12/99
6/11/99
Q9FK003
ppbv
1.21
0.49
ND
1.33
0.06
ND
0.27
0.03
ND
0.02
0.05
0.04
ND
15792
5/24/99
6/10/99
Q9FH026
ppbv
1.26
0.42
0.01
1.02
0.06
ND
0.34
0.02
ND
0.02
0.04
0.03
ND
15831
6/5/99
6/18/99
O9FR017
ppbv
2.15
0.62
ND
1.90
0.08
ND
0.12
0.05
ND
0.02
0.04
0.02
0.00
15924
6/17/99
7/7/99
O9diFOl9
ppbv
1.69
0.50
0.02
1.56
0.08
ND
0.08
0.04
0.01
0.02
0.03
0.03
ND
16029
: 6/29799 T
'-•'• 8/6/99 I:
O9HE012
;ppbv
1.57
0.57
ND
0.26
0.08
ND
0.12
0.05
0.01
0.03
0.03
0.04
ND
16266
:;:;: 7/17/99
8/19/99
O9HQ029
ppbv
3.18
0.80
0.02
1.39
0.12
ND
0.12
0.12
0.01
0.04
0.04
0.04
ND
16256
:: i 7/2370$;
8/19/99;
O9HQ033
ppbv :
2.96
0.81
ND
1.04
0.11
ND
0.11
ND
0.02
0.04
0.04
0.06
ND
16274 !
; ::8/4tesi. ':••••
;8/25/99 ;
G9HX025
ppbv
1.08
0.45
ND
0.92
0.05
ND
0.08
0.05
0.01
0.02
0.04
0.02
ND
u - Concentration is below the detection limit
5 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Underbill, VT
Derivatized Gone. (ug/mL)
SAMPLE fiATE
ANALYSispATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
sovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
16492
8/16/99
9/11/99
69IJ019
ppbv
1.61
0.42
0.01
0.86
0.06
ND
0.07
0.04
0.01
0.02
0.03
0.03
ND
16621
8/28/99
vbib
vdib
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
16802
9/S/99"
1 0/1/99
09I$033
ppbv
1.41
0.47
ND
1.18
0.06
ND
0.06
0.05
0.01
0.02
0.02
0.04
ND
16891
9/21/99
10/13/99
O9JM013
ppbv
0.60
0.29
ND
0.47
0.04
0.004
0.05
0.02
ND
0.02
0.02
0.02
ND
u - Concentration is below the detection limit
-------
FIELD BLANK DATA
Sample site: Underbill, VT
RAW AMOUNT
Derivatized Cone. (ug/mL)
Data File ID
FBID
Sample date
Date Analyzed
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyd(
Q8J#010
1481 7 FB
9/14/98
10/29/98
O9C$012
15546FB
3/13/99
3/30/99
O9HQ009
16267FB
7/17/99
8/18/99
0.08
0.21
0.00
0.37
0.00
0.00
0.50
0.03
0.00
0.00
0.00
0.00
0.00
0.06
0.09
0.00
0.18
0.00
0.00
~ 0.00
0.00
0.00
0.00
0.03
0.01
0.00
0.10
0.08
0.00
0.12
0.01
0.01
0.10
0.03
0.00
0.02
0.00
0.02
0.00
Field Blanks
Underivatized Conc.(total ug)
Data File ID
FBID
Date Analyzed
Q8J#010
1481 7 FB
10/29/98
O9C$012
15546FB
3/30/99 .
O9HQ009
16267FB
8/18/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyd<
0.04
0.16
ND
0.36
ND
ND
0.57
0.05
ND
ND
ND
ND
ND
0.03
0.07
ND
0.17
ND
ND
ND
ND
ND
ND
0.04
0.01
ND
0.07
0.08
ND
0.14
0.01
0.01
0.15
0.05
ND
0.03
ND
0.04
ND
7 of 7
-------
APPENDIX G
1998/1999 CARBONYL RAW MONITORING DATA
-------
1998 UATMP CARBONYLS
Sample Site: Baton Rouge, LA
B2LA
SAMPLE*
SAMPLE DATE
M(kLY£jis DATE
FiLE\NAWiE '" . •. ' • /• - • '
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
14781
9/8/98
10/28/98
Q8J-023
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
14896
9/20/98
11/12/98
Q8KK023
ppbv
1.11
0.60
0.01
0.70
0.10
ND
0.81
0.06
0.02
0.03
ND
0.03
ND
15065
10/2/98
11/16/98
Q8KP008
ppbv
1.63
0.61
0.05
0.46
0.09
ND
0.09
0.07
0.01
0.02
ND
0.02
0.02
15127
10/14/98
11/16/98
Q8KP009
ppbv
3.76
1.68
0.03
2.91
0.23
ND
0.50
0.11
0.02
0.05
0.03
0.04
ND
15168
11/1/98
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15176
1 1/7/99
12/22/98
Q8LU019
ppbv
1.40
0.70
0.04
0.78
0.08
0.05
0.21
0.03
0.01
0.03
0.04
0.02
ND
15188
11/13/98
12/22/98
Q8LU027
ppbv
1.24
0.97
0.02
1.25
0.08
ND
0.27
0.05
0.02
0.02
ND
0.02
ND
u - Concentration is below the detection limit
1 of 6
-------
1998 UATMP CARBONYLS
Sample Site: Baton Rouge, LA
SAMPLE #
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15204
11/19/98
12/22/98
Q8LU029
ppbv
1.52
1.10
0.01
0.74
0.15
ND
0.14
0.08
0.02
0.04
0.03
0.02
ND
15214
11/25/98
12/22/98
Q8LU033
ppbv
1.76
1.11
0.02
1.17
0.11
ND
0.17
0.05
0.03
0.04
0.04
0.02
ND
15244
12/1/98
12/22/98
Q8LU036
ppbv
1.40
0.82
0.01
0.79
0.08
ND
0.21
0.04
0.01
0.02
0.01
0.02
0.01
15366
1/30/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15369
1/30/99
3/16/99
09CO024
ppbv
0.72
0.36
ND
0.50
0.07
0.02
0.02
0.02
ND
0.02
0.02
0.01
ND
15436
2/11/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15438
2/17/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15468
2/25/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
u - Concentration is below the detection limit
-------
1998 UATMP CARBONYLS
Sample Site: Baton Rouge, LA
SAMPLE?
SAMMirbATE
ANALYSIS DATE
RLE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15490
3099
3/i7/$|>
690*3008
ppbv
0.73
0.56
ND
0.79
0.10
0.03
0.04
0.01
ND
0.01
0.02
0.02
ND
15510
3/13/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15533
: 3/19/99
4/1/99
09C%030
ppbv
1.87
0.99
0.02
1.51
0.22
0.06
0.06
0.02
ND
0.04
0.02
0.07
ND
15673
4/19/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15696
4/20/99
5/20/99
O9ES020
ppbv
0.85
0.56
ND
0.40
0.07
0.01
0.04
0.02
ND
0.02
ND
0.02
ND
15698
4/20/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15708
4/26/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15760
4/30/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
u - Concentration is below the detection limit
3 of 6
-------
1998 UATMP CARBONYLS
Sample Site: Baton Rouge, LA
SAMPLE f
SAMPLE DAtE
ANALYSIS DATE
FILE NAME :•••...••.
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15761
4/30/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15757
5/2/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15779
5/25/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15816
6/4/99
6/10/99
Q9FH031
ppbv
2.78
0.36
0.06
0.11
0.10
ND
0.26
0.02
ND
0.03
0,06
0.06
ND
15833
6/11/99
6/19/99
O9FR021
ppbv
1.67
0.47
ND
0.07
0.08
ND
0.27
0.03
0.01
0.04
0.06
0.07
ND
16040
7/5/99
8/6/99
O9HE013
ppbv
2.69
0.95
0.02
0.12
0.18
ND
0.21
0.05
0.02
0.09
0.04
0.17
ND
16134
7/23/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
16247
7/29/99
8/24/99
O9HX011
ppbv
1.89
0.68
ND
0.10
0.09
ND
0.09
0.03
0.01
0.05
0.04
0.08
ND
u - Concentration is below the detection limit
-------
1998 UATMP CARBONYLS
Sample Site: Baton Rouge, LA
SAMPLE*
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
16317
8/10/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
16476
8/22/99
9/11/99
O9IJ020
ppbv
1.21
0.46
0.01
0.07
0.08
ND
0.18
0.02
0.01
0.02
0.02
0.04
ND
16696
9/5/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
16722
9/15/99
10/1/99
O9I$036
ppbv
4.16
1.12
0.004
1.85
0.18
ND
0.19
0.07
0.01
0.03
0.05
0.03
ND
16870
9/27/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
u - Concentration is below the detection limit
5 of 6
-------
FIELD BLANK DATA
Sample site: Baton Rouge, LA
RAW AMOUNT
Derivatized Cone. (ug/mL)
Data File ID
FBID
Sample date
Date Analyzed
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehydc
Q8KK009
14897FB
9/20/98
11/11/98
1.21
0.21
0.02
0.45
0.00
0.00
0.91
0.00
0.00
0.00
0.00
0.04
0.00
O9C%013
15534FB
3/19/99
3/31/99
2.14
1.95
0.00
3.91
0.31
0.09
. 0.05
0.00
0.00
0.00
0.09
0.03
0.00
VOID
15758FB
5/2/99
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15780FB
5/23/99
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
Field Blanks
Underivatized Cone, (total ug)
Data File ID
FBID
Date Analyzed
Q8KK009
14897FB
11/11/98
O9C%013
15534FB
3/31/99
VOID
15758FB
VOID
VOID
15780FB
VOID
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyd«
0.69
0.16
0.02
0.44
ND
ND
1.04
ND
ND
ND
ND
0.06
ND
1.22
1.53
ND
3.81
0.30
0.10
0.06
ND
ND
ND
0.15
0.05
ND
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
6 of 6
-------
1998 UATMP CARBONYLS
Sample site: Beulah, ND
BUND
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15375D1
2/3/99
3/17/99
09CO076
ppbv
1.11
0.62
ND
1.72
0.05
ND
0.05
0.02
ND
0.04
0.02
0.09
ND
15375R1
2/3/99
3/17/99
09C0077
ppbv
1.10
0.63
ND
1.73
0.05
ND
0.04
0.02
ND
0.04
0.01
0.09
ND
15376 D2
2/3/99
3/17/99
09CO078
ppbv
1.01
0.76
0.04
3.71
0.06
ND
0.04
0.03
ND
0.06
0.02
0.18
ND
15376R2
2/3/99
3/17/99
09CO079
ppbv
1.05
0.76
0.04
3.70
0.06
ND
0.04
0.03
ND
0.06
0.02
0.18
ND
15408
2/13/99
3/16/99
09CO032
ppbv
0.98
0.58
ND
0.79
0.07
0.02
0.05
0.01
ND
0.05
0.02
0.10
ND
15430
2/17/99
3/16/99
09CO033
ppbv
0.88
0.56
ND
0.70
0.09
0.02
0.05
0.01
ND
0.04
0.02
0.03
ND
15442
2/23/99
3/16/99
09CO042
ppbv
0.88
0.47
ND
0.68
0.08
0.02
0.04
0.01
ND
0.03
0.02
0.05
ND
15452
3/1/99
3/17/99
O9CQ006
ppbv
0.76
0.43
ND
0.71
0.07
ND
0.02
ND
ND
0.02
0.02
0.09
ND
15498
3/7/99
3/17/99
09CQ007
ppbv
0.81
0.48
ND
0.77
0.07
0.02
0.03
0.01
ND
0.04
0.02
0.05
ND
15538D1
3/13/99
4/1/99
O9C%038
ppbv
0.50
0.28
ND
0.54
0.04
0.01
0.02
0.003
0.002
0.03
ND
0.07
ND
u - Concentration is below the detection limit
of7
-------
1998 UATMP CARBONYLS
Sample site: Beulah, ND
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15538R1
3/13/99
4/1/99
O9C%039
ppbv
0.50
0.28
ND
0.53
0.04
0.01
0.02
0.01
0.002
0.03
0.01
0.07
ND
15539D2
3/13/99
4/1/99
O9C%035
ppbv
1.05
0.59
ND
1.14
0.09
0.01
0.04
0.01
ND
0.05
0.01
0.07
ND
15539R2
3/13/99
4/1/99
O9C%036
ppbv
1.04
0.58
ND
1.13
0.09
0.01
0.04
0.01
ND
0.05
0.01
0.08
ND
15541 D'l
3/19/99
4/1/99
09C%042
ppbv
0.50
0.20
ND
0.34
0.03
0.01
0.01
ND
ND
0.01
0.01
0.06
ND
15541 R1
3/19/99
4/1/99
O9C%043
ppbv
0.50
0.20
ND
0.35
0.03
0.01
0.01
0.003
ND
0.02
0.01
0.06
ND
15543D2
3/19/99
4/1/99
O9C%040
ppbv
1.00
0.52
ND
0.92
0.07
0.02
0.04
0.004
ND
0.04
0.01
0.07
ND
15543 R2
3/19/99
4/1/99
O9C%041
ppbv
1.05
0.52
ND
0.92
0.07
0.02
0.04
0.01
ND
0.03
0.01
0.07
ND
15571
3/25/99
4/14/99
O9DM027
ppbv
0.75
0.45
ND
0.78
0.07
ND
0.02
ND
ND
0.02
0.01
0.02
ND
15641
3/31/99
5/12/99
09EK019
ppbv
0.64
0.41
ND
0.71
0.06
0.02
0.04
0.01
ND
0.02
ND
0.06
ND
15647
4/6/99
5/12/99
O9EK024
ppbv
0.79
0.43
ND
1.09
0.06
0.01
0.03
0.01
ND
0.02
ND
0.04
ND
u - Concentration is below the detection limi
2af7
-------
1998 UATMP CARBONYLS
Sample site: Beulah, ND
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15638
4/12/99
5/19/99
O9ES016
ppbv
0.54
0.37
0.02
0.78
0.05
0.02
0.03
0.01
ND
0.02
ND
0.06
ND
15683D1
4/18/99
5/20/99
O9ES038
ppbv
0.72
0.48
ND
1.07
0.07
0.02
0.03
0.005
ND
0.02
ND
0.04
ND
15683 R1
4/18/99
5/20/99
O9ES039
ppbv
0.75
0.47
ND
1.06
0.07
0.02
0.03
0.007
ND
0.02
ND
0.04
ND
15685 D2
4/18/99
5/20/99
O9ES040
ppbv
0.29
0.22
ND
0.47
0.04
0.01
0.01
0.004
ND
0.01
ND
0.04
ND
15685R2
4/18/99
5/20/99
O9ES041
ppbv
0.29
0.22
ND
0.47
0.03
0.01
0.01
0.005
ND
0.01
ND
0.04
ND
15706
4/24/99
6/4/99
Q9FD015
ppbv
0.70
0.65
0.01.
1.40
0.07
ND
0.29
ND
ND
ND
ND
0.08
ND
15713
4/30/99
6/4/99
Q9FD016
ppbv
1.00
0.67
0.02
1.50
0.06
ND
0.40
ND
ND
0.02
ND
0.06
ND
15728
5/6/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15730
5/6/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15774
5/18/99
6/9/99
Q9FH018
ppbv
1.42
0.69
0.05
1.20
0.09
ND
0.43
0.03
0.025
0.07
0.06
0.10
ND
u - Concentration is below the detection limi
3 of 7
-------
1998 UATMP CARBONYLS
Sample site: Beulah, ND
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15772
5/24/99
6/10/99
Q9FH022
ppbv
1.34
0.57
0.03
1.25
0.08
ND
0.46
0.03
0.032
0.04
ND
0.08
ND
15835
6/11/99
6/18/99
09FR018
ppbv
1.23
0.49
0.04
0.89
0.07
0.01
0.08
0.03
0.01
0.04
0.02
0.09
ND
15900
6/17/99
7/7/99
O9GF017
ppbv
1.86
0.48
0.04
1.09
0.07
ND
0.09
0.04
ND
0.04
0.02
0.07
ND
15930
6/23/99
7/7/99
O9GF022
ppbv
1.76
0.61
0.05
1.47
0.09
ND
0.09
0.03
0.01
0.05
0.03
0.10
ND
15970
6/29/99
7/7/99
O9GF024
ppbv
1.15
0.52
0.03
1.12
0.07
0.01
0.07
0.05
0.01
0.04
0.02
0.06
ND
16004
7/5/99
8/6/99
O9HE014
ppbv
1.21
0.47
0.03
1.17
0.06
ND
0.04
0.02
ND
0.04
0.02
0.09
ND
16136
7/17/99
8/6/99
O9HE029
ppbv
1.27
0.56
0.03
0.95
0.08
ND
0.07
0.03
0.01
0.04
ND
0.08
ND
16147
7/23/99
8/6/99
O9HE034
ppbv
2.14
0.83
0.03
1.87
0.10
ND
0.12
0.05
0.012
0.05
0.02
0.07
ND
16204
7/29/99
8/6/99
O9HE036
ppbv
3.50
1.77
0.04
3.46
0.22
0.01
0.21
0.07
0.04
0.09
0.03
0.14
ND
16282
8/4/99
8/24/99
O9HX013
ppbv
2.71
1.61
0.03
2.18
0.18
ND
0.20
0.07
0.03
0.08
0.03
0.11
ND
u - Concentration is below the detection limi
4 of 7
-------
1998 UATMP CARBONYLS
Sample site: Beulah, ND
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
16315
8/10/99
8/24/99
O9HX014
ppbv
3.44
1.30
0.04
1.91
0.15
ND
0.19
0.06
0.02
0.07
0.03
0.10
ND
16360
8/16/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
16441
8/22/99
9/11/99
O9IJ023
ppbv
2.45
0.86
0.03
1.83
0.10
ND
0.12
0.03
0.01
0.05
0.02
0.09
ND
16600
8/28/99
9/23/99
O9IV022
ppbv
2.21
0.85
0.04
1.45
0.10
ND
0.12
0.03
0.01
0.06
0.03
0.09
ND
16675
9/3/99
9/23/99
O9IV021
ppbv
1.35
0.80
0.06
1.06
0.07
ND
0.09
0.02
0.01
0.04
0.03
0.09
ND
16703
9/9/99
9/23/99
O9IV023
ppbv
1.33
0.48
0.03
1.73
0.05
ND
0.07
0.02
ND
0.04
0.02
0.07
ND
16787 D1
9/15/99
10/2/99
O9IS053
ppbv
1.30
0.46
ND
1.78
0.06
ND
0.07
0.01
ND
0.04
ND
0.08
ND
16787 R1
9/15/99
10/2/99
O9I$054
ppbv
1.29
0.46
ND
1.78
0.06
0.01
0.08
0.02
ND
0.04
ND
0.07
ND
16789D2
9/15/99
10/2/99
09I$055
ppbv
1.28
0.44
ND
1.59
0.06
ND
0.07
0.01
ND
0.03
ND
0.06
ND
16789 R2
9/15/99
10/2/99
O9IS056
ppbv
1.24
0.42
ND
1.53
0.06
ND
0.07
0.01
ND
0.03
ND
0.05
ND
16800
9/21/99
10/13/99
O9JM019
ppbv
1.63
0.72
0.02
2.20
0.10
0.01
0.12
0.03
0.01
0.04
ND
0.05
ND
u - Concentration is below the detection limi
5 Of 7
-------
1998 UATMP CARBONYLS
Sample site: Beulah, ND
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
16839 D1
9/27/99
10/14/99
O9JM026
ppbv
0.99
0.39
0.02
0.93
0.05
0.01
0.06
0.02
ND
0.03
0.02
0.05
ND
16839 R1
9/27/99
10/14/99
O9JM027
ppbv
1.02
0.39
0.02
0.96
0.05
0.01
0.06
0.02
ND
0.03
0.02
0.06
ND
16841 D2
9/27/99
10/14/99
O9JM028
ppbv
1.10
0.38
0.02
0.88
0.05
0.01
0.07
0.02
0.01
0.02
0.02
0.04
ND
16841 R2
9/27/99
10/14/99
O9JM029
ppbv
1.10
0.38
0.01
0.88
0.05
0.01
0.07
0.02
0.01
0.03
0.01
0.04
ND
u - Concentration is below the detection limi
6-C?7
-------
FIELD BLANK DATA
Sample site: Beulah, ND
RAW AMOUNT
Derivatized Cone. (ug/mL)
Data File ID
FBID
Sample date
Date Analyzed
O9ES007
15639FB
4/12/99
5/19/99
Q9FD008
1571 4 FB
4/30/99
6/4/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldeh
0.02
0.08
0.05
0.14
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.10
0.10
0.00
0.00
0.29
0.05
0.29
0.00
0.00
0.00
0.00
0.05
0.00
Q9FH009
15775FB
5/18/99
6/9/99
0.08
0.10
0.00
0.17
0.00
0.00
0.39
0.00
0.00
0.00
0.00
0.00
0.00
Field Blanks
Underivatized Cone, (total ug)
Data File ID
FBID
Date Analyzed
O9ES007
15639FB
5/19/99
Q9FD008
1571 4 FB
6/4/99
Q9FH009
15775FB
6/9/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldeh
0.01
0.07
0.05
0.14
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.05
0.08
ND
0.00
0.29
0.05
0.33
ND
ND
ND
ND
0.07
ND
0.05
0.08
ND
0.17
ND
ND
0.45
ND
ND
ND
ND
ND
ND
7 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Brattleboro, Vermont
BRVT
Derivatized ;Gbncv (tig/fnL)
sWf»Li:DAfi^x>::;;';v- " " . '
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
14685
9/2/98
10/27/98
Q8J-012
ppbv
1.22
0.44
0.02
0.79
0.07
ND
0.24
0.04
0.01
0.02
0.02
0.04
ND
14812
9/14/98
10/28/98
Q8J-029
ppbv
1.56
0.79
0.09
0.90
0.10
ND
0.11
0.07
0.01
0.03
0.04
0.05
ND
15055
9/26/98
11/12/98
Q8KK024
ppbv
1.41
0.71
ND
1.16
0.09
ND
0.11
0.08
0.02
0.03
0.04
0.06
ND
15114
10/8/98
11/16/98
Q8KP012
ppbv
1.08
0.66
0.05
0.69
0.08
ND
0.27
0.03
0.01
0.03
ND
0.03
ND
15138
10/20/98
11/16/98
Q8KP013
ppbv
1.00
0.52
ND
1.18
0.07
ND
0.27
0.03
ND
0.02
ND
0.03
ND
15156
11/1/98
11/25/98
Q8KW021
ppbv
0.72
0.36
0.01
0.86
0.05
ND
0.28
0.03
ND
0.02
0.02
0.03
ND
15196
11/13/98
11/25/98
Q8KW025
ppbv
1.17
0.75
0.03
1.33
0.09
ND
0.22
0.05
0.015
0.02
0.03
0.03
0.01
u - Concentration is below the detection limit
1 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Brattleboro, Vermont
Derivatized piihb; (ug/mU)
S^MRLtlATE-'.-' "' . ' .
All/VLYSIS iDATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15238
11/25/98
12/21/98
Q8LU010
ppbv
1.11
0.56
0.02
1.16
0.07
ND
0.11
0.05
0.01
0.02
0.03
0.03
ND
15252
12/7/98
12/21/98
Q8LU014
ppbv
1.12
0.74
0.01
0.94
0.10
0.04
0.13
0.03
0.02
0.03
0.03
0.03
ND
15283
12/19/98
1/8/99
Q9AG034
ppbv
1.32
0.87
0.04
1.12
0.10
0.01
0.14
0.05
0.01
0.02
0.04
0.03
ND
15305
12/3-(/9£t
2/20/99
O9BS016
ppbv
2.26
1.17
0.05
1.42
0.12
0.03
0.19
0.07
0.02
0.04
0.05
0.05
ND
15319
1/i|/93
2/26799
O9BS022
Ppbv
1.69
1.08
0.03
1.40
0.13
0.02
0.13
0.07
0.01
0.03
0.06
0.05
ND
15350 D1
1/24/99
2/20/99
09BS027
ppbv
0.88
0.56
0.01
0.72
0.06
0.01
0.06
0.04
0.01
0.02
0.02
0.03
ND
; 15350 R1
: :::i/i4/si-: -':
2/20799 :
d9BS028
ppbv
0.90
0.57
0.01
0.74
0.06
0.01
0.06
0.04
0.01
0.02
0.02
0.03
ND
u - Concentration is below the detection limit
2 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Brattleboro, Vermont
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15352D2
1/24/99
2/20/99
O9BS029
ppbv
0.93
0.58
0.01
0.75
0.06
0.01
0.06
0.04
0.010
0.02
0.03
0.04
ND
15352 R2
1/24/99
2/20/99
O9BS030
ppbv
0.89
0.58
0.01
0.75
0.06
0.01
0.06
0.05
0.01
0.02
0.03
0.04
ND
15414
2/5/99
3/16/99
09CO026
PPPV
0.83
0.41
ND
0.71
0.08
0.04
0.03
0.02
ND
0.04
0.03
0.02
ND
15444
2/15/99
3/16/99
09CO034
PpbV
1.47
0.96-
ND
2.62
0.15
0.12
0.07
0.06
ND
0.04
0.06
0.06
ND
15484
3/1/99
3/16/99
09CO051
Ppbv
1.36
0.71
ND
1.09
0.11
0.09
0.05
0.04
ND
0.04
0.05
0.05
ND
15548
3/13/99
3/31/99
O9C%020
ppbv
1.02
0.54
ND
0.76
0.10
0.03
0.05
0.04
ND
0.03
0.02
0.03
ND
15588D1
3/25/99
4/14/99
O9DM044
:Ppbv
0.93
0.42
ND
0.78
0.07
ND
0.03
0.02
ND
0.02
0.02
0.02
ND
u - Concentration is below the detection limit
3oL7
-------
1998 UATMP CARBONYLS
Sample Site: Brattleboro, Vermont
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15588R1
3/25/99
4/14/99
O9DM045
ppbv
0.95
0.43
ND
0.79
0.07
ND
0.03
0.02
ND
0.02
0.02
0.02
ND
15590 D2
3&S/09
4/14/913
O9DM046
ppbv
0.93
0.40
ND
0.75
0.07
ND
0.03
0.02
ND
0.02
0.02
0.02
ND
15590R2
3/i>5/99
M4/9|
09DM048
ppbv
0.93
0.40
ND
0.75
0.07
ND
0.03
0.02
ND
0.02
0.02
0.02
ND
15657
4/6)99 ;
5/12/99
P9EK025
ppbv
1.57
0.80
ND'
1.37
0.12
0.04
0.06
0.03
ND
0.02
0.00
0.04
ND
15827
5^2/69
,: ;: V0!D
vciib
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15829
5/12/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15790
5/18/99
6/9/99
Q9FH019
ppbv
1.83
1.14
0.04
0.76
0.13
ND
0.26
0.06
0.047
0.05
0.04
0.11
ND
u - Concentration is below the detection limit
4 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Brattleboro, Vermont
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15837
5/30/99
6/18/99
O9FR013
ppbv
3.54
1.51
0.04
1.41
0.24
0.01
0.19
0.16
0.032
0.10
0.06
0.17
0.00
15839
6/5/99
6/18/99
O9FR014
ppbv
2.50
0.96
0.02
2.01
0.15
0.01
0.16
0.13
0.02
0.06
0.07
0.11
ND
15920
6/17/99
7/7/99
O9GF016
ppbv
2.23
0.73
0.01
1.50
0.11
ND
0.13
0.09
0.02
0.04
0.05
0.06
ND
16023
6/29/99
8/5/99
O9HE009
ppbv
1.94
0.78
0.01
0.22
0.08
ND
0.07
0.04
0.02
0.05,
0.04
0.06
ND
16270
7/17/99
8/19/99
O9HQ025
ppbv
2.93
0.72
0.02
0.18
0.14
ND
0.15
0.06
0.03
0.11
0.06
0.14
ND
16253
7/23/99
8/19/99
O9HQ030
ppbv
3.55
1.12
ND
1.35
0.16
0.01
0.18
ND
ND
0.08
0.07
0.11
ND
16311
8/2/99
8/24/99
O9HX012
ppbv
3.15
0.82
ND
1.72
0.09
ND
0.17
0.16
0.02
0.07
0.07
0.08
ND
u - Concentration is below the detection limit
5 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Brattleboro, Vermont
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
16497
8/W99
9/111/99
O9iJfrl6
ppbv
1.85
0.60
ND
1.15
0.08
ND
0.14
0.04
ND
0.04
0.04
0.06
ND
16612
8728/919
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
16614
973/99
9/2"3/99
O9IV027
ppby
2.82
0.73
ND
1.26
0.12
ND
0.11
0.06
0.01
0.05
0.05
0.08
ND
16804
9/9/99
10/1/99
O9I$034
ppbv
2.76
0.89
ND
0.81
0.10
ND
0.09
0.04
ND
0.04
0.03
0.08
ND
169Q4
•; 9/2:1)99
10/1^/99
O9JMOT1
ppby :
1.08
0.46
0.01
0.59
0.07
0.01
0.10
0.04
ND
0.03
0.05
0.05
0.01
u - Concentration is below the detection limit
6 of 7
-------
FIELD BLANK DATA
Sample site: Brattleboro, VT
RAW AMOUNT
Derivatized Cone. (ug/mL)
Data File ID
FBID
Sample date
Date Analyzed
Q8J-008
1481 3 FB
9/14/98
10/27/98
O9C%008
15549FB
3/13/99
3/31/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.03
0.05
0.00
0.34
0.00
. 0.00
0.28
0.00
0.00
0.00
0.00
0.02
0.00
0.19
0.10
0.03
0.17
0.02
0.00
0.01
0.04
0.00
0.01
0.02
0.03
0.00
Field Blanks
Underivatized Cone.(total ug)
Data File ID
FBID
Date Analyzed
Q8J-008
1481 3 FB
10/27/98
O9C%008
15549FB
3/31/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.02
0.04
ND
0.33
ND
ND
0.33
ND
ND
ND
ND
0.02
ND
0.11
0.08
0.03
0.16
0.02
ND
0.01
0.06
ND
0.02
0.03
0.05
ND
7 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Burlington, VT
BUVT
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
14678
9/2/98
10/27/98
Q8J-013
ppbv
2.56
0.85
0.10
1.00
0.10
ND
0.11
0.05
ND
0.02
0.04
0.01
ND
14819
9/14/98
10/29/98
Q8J#019
ppbv
1.86
0.79
0.20
0.66
0.09
ND
0.10
0.06
0.01
0.03
0.04
0.02
ND
15084
9/26/98
11/12/98
Q8KK025
ppbv
2.68
1.17
ND
1.03
0.13
ND
0.18
0.06
0.02
0.04
0.04
0.04
0.02
15108
10/8/98
11/16/98
Q8KP014
ppbv
2.67
0.98
0.03
1.19
0.12
0.05
0.48
0.08
ND
0.03
0.05
0.03
0.01
15148
10/20/98
11/16/98
Q8KP016
ppbv
3.10
0.83
0.02
1.89
0.11
ND
0.41
0.06
ND
0.02
0.04
0.02
ND
15154
11/1/98
11/25/98
Q8KW022
ppbv
1.97
0.72
0.03
1.07
0.07
ND
0.34
0.06
0.02
0.02
0.04
0.02
0.01
15198
11/13/98
11/25/98
Q8KW027
ppbv
2.75
0.87
0.02
1.60
0.09
ND
0.17
0.06
ND
0.03
0.06
0.02
0.02
15236
11/25/98
12721/98
Q8LU011
ppbv
1.62
0.59
0.02
0.88
0.07
0.03
0.10
0.04
0.01
0.02
0.03
0.02
ND
15250
12/7/98
12/22/98
Q8LU016
ppbv
1.87
0.69
0.02
1.22
0.09
ND
0.12
0.05
0.01
0.02
0.04
0.02
ND
u - Concentration is below the detection limit
1 of 6
-------
1998 UATMP CARBONYLS
Sample Site: Burlington, VT
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Folualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15285
12/19/98
1/8/99
09AG035
ppbv
1.65
0.90
0.04
0.93
0.10
0.004
0.11
0.05
0.01
0.02
0.03
0.02
ND
15311
12/31/98
2/20/99
09BS017
ppbv
1.66
1.01
0.03
0.90
0.11
0.01
0.09
0.06
0.01
0.03
0.03
0.03
0.003
15327
1/12/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15355D1
1/24/99
2/20/99
O9BS031
ppbv
2.01
0.75
0.01
0.84
0.09
0.01
0.08
0.05
0.01
0.02
0.04
0.04
ND
15355R1
1/24/99
2/20/99
O9BS032
ppbv
2.01
0.75
0.01
0.84
0.09
0.004
0.07
0.05
0.01
0.02
0.04
0.04
ND
15357D2
1/24/99
2/20/99
O9BS033
ppbv
2.04
0.73
0.01
0.82
0.08
0.005
0.08
0.04
0.01
0.02
0.04
0.03
ND
15357R2
1/24/99
2/20/99
O9BS034
ppbv
2.04
0.73
0.01
0.82
0.09
0.005
0.08
0.05
0.009
0.02
0.04
0.04
ND
15406
2/5/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15450
2/17/99
3/16/99
09CO035
ppbv
2.53
1.03
ND
1.23
0.16
0.11
0.06
0.07
ND
0.03
0.05
0.02
ND
u • Concentration is below the detection limit
-------
1998 UATMP CARBONYLS
Sample Site: Burlington, VT
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15478
2/23/99
3/16/99
09CO043
ppbv
2.16
0.94
ND
0.93
0.15
0.10
0.05
0.05
ND
0.03
0.04
0.02
ND
15482
3/1/99
3/16/99
09CO052
ppbv
2.90
1.06
ND
1.15
0.17
ND
0.06
0.07
ND
ND
0.07
0.04
ND
15554
3/13/99
3/31/99
O9C%021
ppbv
2.20
0.77
ND
0.83
0.12
0.05
0.04
0.03
ND
0.02
0.02
0.01
ND
15603 D1
3/25/99
5/12/99
O9EK033
ppbv
2.19
0.57
ND
0.98
0.08
0.05
0.03
0.04
ND
0.01
0.02
0.02
ND
15603R1
3/25/99
5/12/99
O9EK034
ppbv
2.20
0.57
ND
0.96
0.08
0.05
0.03
0.04
ND
0.01 j
0.02
0.01
ND
15605D2
3/25/99
5/12/99
O9EK035
ppbv
2.01
0.54
ND
0.91
0.07
0.04
0.03
0.04
ND
0.01
0.02
0.01
ND
15605 R2
3/25/99
5/12/99
O9EK036
ppbv
2.01
0.54
ND
0.91
0.07
0.04
0.03
0.04
ND
0.01
0.02
0.01
0.004
15645
4/6/99
5/12/99
O9EK027
ppbv
3.16
1.12
ND
1.28
0.16
0.08
0.08
0.05
ND
0.02
0.02
0.03
ND
15677
4/18/99
5/19/99
O9ES017
ppbv
2.47
0.74
ND
0.94
0.11
0.08
0.07
0.04
ND
0.02
0.01
0.02
ND
u - Concentration is below the detection limit
3 of 6
-------
1998 UATMP CARBONYLS
Sample Site: Burlington, VT
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15734
4/30/99
6/5/99
Q9FD017
ppbv
4.99
1.67
0.02
2.02
0.20
ND
0.59
0.15
0.04
0.04
0.08
0.11
0.01
15796D1
5/12/99
6/10/99
Q9FH036
ppbv
3.25
1.05
0.02
1.69
0.13
ND
0.29
0.07
0.02
0.03
0.06
0.02
ND
15796 R1
5/12/99
6/10/99
Q9FH037
ppbv
3.25
1.09
0.04
1.69
0.11
ND
0.31
0.07
0.04
0.03
0.09
0.02
ND
15798D2
5/12/99
6/10/99
Q9FH038
ppbv
3.52
1.13
0.02
1.75
0.14
ND
0.29
0.08
ND
0.04
0.07
0.04
ND
15798 R2
5/12/99
6/10/99
Q9FH039
ppbv
3.54
1.09
0.02
1.78
0.14
ND
0.27
0.06
0.02
0.04
0.07
0.04
0.01
15794
5/24/99
6/10/99
Q9FH023
ppbv
3.26
1.04
0.02
1.24
0.12
ND
0.50
0.07
0.02
0.04
0.04
0.05
ND
15841
6/5/99
6/18/99
O9FR016
ppbv
4.43
1.43
ND
2.26
0.20
ND
0.20
0.11
0.02
0.05
0.05
0.05
0.01
15922
6/17/99
7/7/99
O9GF018
ppbv
4.34
1.09
0.03
1.99
0.15
ND
0.15
0.09
0.01
0.04
0.05
0.04
0.01
16025
6/29/99
8/5/99
O9HE010
ppbv
1.72
0.07
0.006
0.08
0.02
ND
ND
0.06
ND
0.02
0.04
0.02
ND
u - Concentration is below the detection limit
4 of 6
-------
1998 UATMP CARBONYLS
Sample Site: Burlington, VT
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
16261
7/17/99
8/19/99
O9HQ027
ppbv
5.59
1.63
0.03
0.18
0.25
0.01
0.19
0.05
0.02
0.06
0.06
0.08
ND
16263
7/29/99
8/19/99
09HQ031
ppbv
6.52
1.47
0.02
0.28
0.21
0.02
0.23
0.16
0.03
0.07
0.06
0.06
ND
16278
8/4/99
8/24/99
09HX015
ppbv
2.75
1.06
0.09
0.39
0.14
ND
0.22
0.06
0.02
0.04
0.04
0.03
0.009
16495
8/16/99
9/11/99
09IJ017
ppbv
4.18
1.38
ND
1.50
0.17
ND
0.23
0.08
0.03
0.07 '
0.06
0.06
ND
16616
8/28/99
9/23/99
09IV025
ppbv
4.61
1.01
ND
0.57
0.18
ND
0.13
0.06
ND
0.05
0.05
0.06
ND
16806
9/9/99
10/1/99
O9I$038
ppbv
3.39
1.00
0.01
1.32
0.12
ND
0.12
0.11
ND
0.06
0.06
0.06
ND
16902
9/21/99
10/13/99
O9JM012
ppbv
1.19
0.50
0.03
0.62
0.07
0.01
0.07
0.05
ND
0.03
0.05
0.03
ND
u - Concentration is below the detection limit
5 of 6
-------
FIELD BLANK DATA
Sample site: Burlington, VT
RAW AMOUNT
Derivatized Cone. (ug/mL)
Data File ID
FBID
Sample date
Date Analyzed
Q8J#008
14820FB
9/14/98
10/29/98
09C%009
15555FB
3/13/99
3/31/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.03
0.21
0.00
0.38
0.00
0.00
0.32
0.00
0.00
0.00
0.00
0.00
0.00
0.12
0.10
0.05
0.16
0.04
0.00
0.00
0.00
0.00
0.01
0.02
0.00
0.00
Field Blanks
Underivatized Cone, (total ug)
Data File ID
FBID
Date Analyzed
Q8J#008
14820FB
10/29/98
O9C%009
15555FB
3/31/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.02
0.17
ND
0.38
ND
ND
0.36
ND
ND
ND
ND
ND
ND
0.07
0.08
0.04
0.15
0.04
ND
ND
ND
ND
0.01
0.04
ND
ND
6 of 6
-------
1998 UATMP CARBONYLS
Sample Site: Camden, NJ
CANJ
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
14770
9/8/98
10/28/98
Q8J-024
ppbv
2.46
1.20
0.02
1.46
0.19
ND
0.54
0.04
0.02
0.27
ND
0.07
ND
14890
9/14/98
10/28/98
Q8J-030
ppbv
3.95
1.67
0.08
1.19
0.32
ND
0.49
0.10
0.02
0.23
0.02
0.10
ND
14970
9/20/98
11/12/98
Q8KK033
ppbv
3.80
2.44
0.20
1.26
0.39
ND
0.39
0.09
0.02
0.28
0.04
0.07
ND
15086
10/2/98
11/16/98
Q8KP017
ppbv
3.20
1.77
0.03
3.01
0.36
ND
1.09
0.05
0.04
0.55
0.03
0.12 .
ND
15121
10/14/98
11/16/98
Q8KP018
ppbv
2.03
1.19
0.03
1.93
0.18
ND
0.77
0.04
ND
0.18
ND
0.05
ND
15144
10/26/98
11/25/98
Q8KW014
ppbv
4.37
2.71
0.06
3.73
0.45
ND
1.23
0.12
0.04
0.64
0.04
0.14
ND
15178
11/7/98
12/22/98
Q8LU020
ppbv
2.64
1.96
0.04
2.10
0.37
0.04
0.71
0.07
0.059
0.62
0.06
0.05
0.02
u - Concentration is below the detection limit
1 Of 7
-------
1998 UATMP CARBONYLS
Sample Site: Camden, NJ
Derivatized Cone. (ug/mL) ; :
SAMPLE-DATE ' ":- ?" ' '. :' : ' ;- "": : ' x - "•' '" :-
A^AI-Y^IS PATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15212
11/19/98
12/212/98
QSLUMo
ppbv
2.78
1.87
0.02
3.13
0.29
ND
0.63
0.06
0.04
0.43
0.04
0.03
ND
15218
12)1/98
•:V&!J|.-;.
•• vSici
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15228
12/1J/98
12/22/98
Q8LU034
ppbv
1.92
1.18
0.02
1.75
0.12
ND
0.26
0.04
0.01
0.03
ND
0.06
ND
15263
12/13/98
1/8/99
O9AG028
ppbv
2.81
1.81
0.02
2.28
0.36
0.02
0.59
0.09
0.04
0.52
0.05
0.18
ND
15277
12/25/98
1/8/99
O9AG039
ppbv
3.23
1.95
0.04
1.96
0.48
0.02
0.71
0.05
0.03
0.68
0.04
0.17
ND
15317
1/6/99
2/20/99
O9BS020
ppbv
2.46
1.53
0.02
1.68
0.41
0.02
0.51
0.05
0.03
0.46
0.04
0.13
ND
u - Concentration is below the detection limit
2nf7
-------
1998 UATMP CARBONYLS
Sample Site: Camden, NJ
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15378D1
1/30/99
2/20/99
O9BS044
ppbv
2.39
1.18
0.005
1.93
0.22
0.01
0.33
0.05
0.01
0.25
0.05
0.09
ND
15378R1
1/30/99
2/20/99
O9BS045
ppbv
2.39
1.18
0.005
1.93
0.21
0.01
0.33
0.05
0.02
0.25
0.05
0.09
ND
15380D2
1/30/99
2/20/99
O9BS046
ppbv
2.30
1.13
0.005
1.83
0.20
0.01
0.31
0.05
0.01
0.23
0.05
0.08
ND
15380R2
1/30/99
2/20/99
09BS047
ppbv
2.31
1.14
0.005
1.83
0.20
0.01
0.31
0.05
0.02
0.23
0.04
0.07 '
ND
15454
2/17/99
3/16/99
09C0049
ppbv
3.68
1.78
ND
2.92
0.34
0.12
0.26
0.06
0.05
0.23
0.09
0.10
ND
15464
2/23/99
3/16/99
09CO045
ppbv
2.75
1.56
ND
2.79
0.40
0.06
0.49
0.04
0.09
0.49
0.04
0.13
ND
15512
3/7/99
3/17/99
O9CQ009
ppbv
2.44
1.11
ND
1.33
0.24
0.05
0.25
0.02
0.05
0.23
0.02
0.05
ND
u - Concentration is below the detection limit
3 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Camden, NJ
Derivatized Cone. (ug/mL)
SAMPLE DATE :
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
1553(5
3/13^99
3/3i/96
O9C6/o622
ppbv
3.11
1.30
ND
1.65
0.31
0.04
0.34
0.04
0.06
0.32
ND
0.06
ND
1552501
3/25/99 ;
5/12/99
09EK038
ppbv
2.50
1.12
0.04
1.96
0.23
0.04
0.21
0.02
ND
0.14
0.001
0.05
ND
15625R1
3/25/99
5/12/99
O9EK039
ppbv
2.57
1.12
0.04
1.96
0.23
0.04
0.22
0.02
ND
0.13
0.002
0.05
ND
15627 D2
3/25/99
5/12/99
O9EK040
ppbv
2.51
1.11
0.02
1.95
0.23
0.03
0.21
0.03
ND
0.12
0.004
0.05
ND
15627R2
3/25/99
5/12/99
O9EK041
ppbv
2.57
1.12
0.02
1.96
0.23
0.03
0.21
0.03
ND
0.12
0.003
. 0.05
ND
15687
4/18/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15710
4/30/99
6/5/99
Q9FD018
ppbv
1.51
0.82
0.01
1.72
0.12
ND
0.36
0.03
ND
0.12
0.04
0.07
ND
u - Concentration is below the detection limit
4 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Camden, NJ
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15787
5/24/99
6/10/99
Q9FH024
ppbv
3.69
2.16
0.03
2.09
0.36
ND
1.10
0.11
0.112
0.50
0.07
0.11
ND
15903
6/5/99
7/6/99
O9GF013
ppbv
4.76
2.32
0.02
2.97
0.44
0.01
0.50
0.11
0.03
0.35
0.04
0.15
ND
15996
6/17/99
7/28/99
O9G1014
ppbv
2.49
1.58
ND
2.57
0.49
ND
0.59
0.08
0.03
0.51
0.03
0.20
ND
16001
7/5/99
8/6/99
O9HE016
ppbv
8.75
3.13
0.04
1.43
0.74
ND
0.89
0.23
0.05
0.78
0.06
0.29
ND
16037
7/11/99
8/6/99
09HE020
ppbv
4.03
1.81
0.02
2.11
0.55
ND
0.70
0.09
0.04
0.67
ND
0.23
ND
16188
7/23/99
8/6/99
09HE035
ppbv
8.02
3.25
0.04
1.80
0.69
0.02
0.54
0.13
0.03
0.30
0.07
0.14
ND
16242
8/4/99
8/24/99
O9HX016
ppbv
5.73
2.69
0.02
1.13
0.48
0.01
0.54
0.13
0.04
0.34
0.09
0.15
ND
u - Concentration is below the detection limit
5 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Camden, NJ
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
16364
8/16/99
8/25/99
O9HX017
ppbv
5.33
2.62
0.02
0.94
0.50
0.01
0.54
0.17
0.03
0.40
0.07
0.15
ND
16602
8/28/99
9/23/99
O9IV019
ppbv
6.08
2.85
0.03
0.94
0.57
0.03
0.53
0.08
0.03
0.40
0.03
0.15
0.01
16714
9/9/99
9/23/99
O9IV020
ppbv
3.99
2.10
0.04
1.55
0.42
0.02
0.53
0.09
0.03
0.33
0.03
0.16
ND
16792 D1
9/15/99
10/2/99
O9IS048
ppbv
2.87
1.71
ND
1.21
0.37
ND
0.38
0.08
0.03
0.31
0.03
0.13
ND
16792 R1
9/15/99
10/2/99
O9IS049
ppbv
2.87
1.64
ND
1.21
0.37
ND
0.35
0.05
0.04
0.31
0.03
0.13
ND
16793 D2
9/15/99
10/2/99
O9I$051
ppbv
2.79
1.67
ND
1.26
0.36
0.005
0.35
0.05
0.02
0.30
0.04
0.12
ND
16793R2
9/15/99
10/2/99
O9I$052
ppbv
2.85
1.65
ND
1.27
0.37
0.01
0.36
0.06
0.03
0.31
0.04
0.13
ND
u - Concentration is below the detection limit
6 Of 7
-------
FIELD BLANK DATA
Sample site: Camden, NJ
RAW AMOUNT
Derivatized Cone. (ug/mL)
Data File ID
FBID
Sample date
Date Analyzed
Q8J-009
14891 FB
9/14/98
10/27/98
Q8KK010
14971 FB
9/20/98
11/11/98
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.09
0.07
0.00
0.35
0.00
0.00
0.46
0.00
0.00
0.00
0.00
0.02
0.00
0.15
0.08
0.00
0.41
0.00
0.00
0.69
0.00
0.00
0.00
0.00
0.00
0.00
Q8KK018
15087FB
10/2/98
11/12/98
0.07
0.07
0.00
0.36
0.00
0.00
0.56
0.00
0.00
0.00
0.00
0.02
0.00
Q9FD009
15711 FB
4/30/99
6/4/99
Q9FH011
15788FB
5/24/99
6/9/99
0.05
0.10
0.00
0.00
0.22
0.04
0.27
0.00
0.04
0.00
0.00
0.16
0.00
0.28
0.15
0.00
0.28
0.00
0.00
0.63
0.00
0.00
0.00
0.00
0.00
0.00
O9GI008
16038FB
7/11/99
6/19/97
09HX007
16243FB
8/4/99
7/15/97
0.09
0.06
0.00
0.10
0.00
0.00
0.05
0.02
0.02
0.02
0.00
0.01
0.00
0.08
0.06
0.00
0.09
0.01
0.00
0.00
0.00
0.00
0.02
0.00
0.02
0.00
O9IV007
16603FB
8/28/99
7/31/97
0.07
0.14
0.00
0.16
0.01
0.00
0.00 "
0.02
0.00
0.02
0.00
0.03
0.00
Field Blanks
Underivatized Cone, (total ug)
Data File ID
FBID
Date Analyzed
Q8J-009
14891 FB
10/27/98
P8KK010
14971 FB
11/11/98
Q8KK018
15087FB
11/12/98
Q9FD009
15711 FB
6/4/99
Q9FH011
15788FB
6/9/99
O9GI008
16038FB
6/19/97
09HX007
16243FB
7/15/97
O9IV007
16603FB
7/31/97
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.05
0.05
ND
0.34
ND
ND
0.53
ND
ND
ND
ND
0.03
ND
0.09
0.07
ND
0.40
ND
ND
0.79
ND
ND
ND
ND
ND
ND
0.04
0.06
ND
0.35
ND
ND
0.64
ND
ND
ND
ND
0.03
ND
0.03
0.08
ND
0.00
0.21
0.05
0.31
ND
0.05
ND
ND
0.23
ND
0.16
0.12
ND
0.27
ND
ND
0.72
ND
ND
ND
ND
ND
ND
0.07
0.06
ND
0.13
ND
ND
0.08
0.03
0.03
0.03
ND
0.02
ND
0.06
0.06
ND
0.10
0.01
ND
ND
ND
ND
0.03
ND
0.04
ND
0.05
0.14
ND
0.20
0.02
ND
ND
0.04
ND
0.04
ND
0.05
ND
7 of 7
-------
1998 UATMP CARBONYLS
Sample Site: El Paso, TX
EPTX
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Folualdehydes
Hexaldehyde
2,5-DimethyIbenzaldehyde
14894
9/14/98
10/29/98
Q8J#020
ppbv
14.32d
4.83
0.12
1.60
0.31
0.02
0.40
0.33
0.33
0.16
0.26
0.23
0.02
15001
9/20/98
11/12/98
Q8KK034
ppbv
3.68
1.34
0.03
1.18
0.14
ND
0.34
0.07
0.01
0.04
0.03
0.03
0.01
15067
10/2/98
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15129
10/2/98
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15130
10/14/98
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15150
10/26/98
11/25/98
Q8KW016
ppbv
20.13d
4.36
0.40
0.72
0.25
0.05
0.42
0.38
0.32
0.19
0.31
0.25
0.02
15184
11/7/98
12/22/98
Q8LU021
ppbv
1 1 .84d
2.23
0.11
1.92
0.12
0.02
0.23
0.20
0.18
0.10
0.25
0.15
0.02
15208
11/19/98
12/22/98
Q8LU028
ppbv
3.44
1.10
0.03
1.33
0.10
ND
0.14
0.07
0.04
0.05
0.05
0.02
0.02
u - Concentration is below the detection limit
d - Concentration determined using a
dilution factor
1 2f 7
-------
1998 UATMP CARBONYLS
Sample Site: El Paso, TX
Derivatized Cone. (ug/mL) j; :
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15234
; '• t27i/98 •'•:•;
12/22/98 '•:•
Q8LU035
ppbv
2.94
1.19
0.02
1.48
0.11
ND
0.14
0.08
0.02
0.03
0.05
0.01
ND
15267
121/113/98
1/sM
O9AG029
ppbv
4.09
2.42
0.04
2.25
0.26
0.02
0.22
0.11
0.01
0.05
0.10
0.05
ND
15291
12/25/98
1/8/99
O9AG646
ppbv
5.38
2.43
0.05
2.57
0.25
0.02
0.24
0.13
0.02
0.07
0.13
0.06
ND
15344
1/6/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID ,
VOID
15390
1/30/99
3/16/99
09C0023
ppbv
2.80
1.20
ND
1.32
0.17
0.07
0.07
0.06
ND
0.04
0.05
0.03
ND
15402 D1
2/11/99
3/16/99
09CO063
ppbv
1.46
0.54
ND
0.51
0.08
0.05
0.03
0.02
ND
0.02
0.03
0.01
ND
15402R1
2/11/99
3/16/99
09CO064
ppbv
1.48
0.54
ND
0.51
0.09
0.05
0.03
0.03
ND
0.03
0.03
0.01
ND
u - Concentration is below the detection limit
d - Concentration determined using a
dilution factor
2 of 7
-------
1998 UATMP CARBONYLS
Sample Site: El Paso, TX
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Folualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15404 D2
2/11/99
3/16/99
09CO065
ppbv
1.28
0.50
ND
0.49
0.07
0.05
0.03
0.02
ND
0.02
0.02
0.01
ND
15404R2
2/11/99
3/16/99
09CO066
ppbv
1.28
0.50
ND
0.49
0.08
0.05
0.03
0.03
ND
0.03
0.02
0.01
ND
15434
2/17/99
3/16/99
09CO036
ppbv
6.41d
2.57
ND
2.52
0.24
0.10
0.12
0.15
ND
ND
0.09
0.14
ND
15466
2/23/99
3/16/99
09CO046
ppbv
6.01
2.38
0.02
1.97
0.23
0.14
0.11
0.14
ND
0.15
0.08
0.13
ND
15456
3/1/99
3/17/99
O9CQ010
ppbv
2.94
0.86
0.01
1.11
0.13
0.06
0.05
0.04
ND
0.02
0.04
0.03
ND
15496
3/7/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15528
3/13/99
3/31/99
O9C%023
ppbv
2.55
0.96
ND
1.40
0.15
0.06
0.06
0.05
ND
0.02
0.04
0.02
ND
15526
3/19/99
4/1/99
O9C%028
ppbv
3.04
1.13
0.02
1.40
0.18
0.07
0.07
0.05
ND
0.02
0.04
0.03
0.01
u - Concentration is below the detection limit
d - Concentration determined using a
dilution factor
3 of 7
-------
1998 UATMP CARBONYLS
Sample Site: El Paso, TX
Derivatized Cone. (ug/mL) •
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15617;
3/31/99
5/12^9; 1
oiEkoio
ppbv
2.57
0.70
ND
0.95
0.08
0.03
0.05
0.04
ND
0.02
0.01
0.02
ND
15635
;4/6/99 :••' :
5/12/99;
O9EKb28
ppbv
5.80
2.78
0.02
2.45
0.28
0.09
0.15
0.16
ND
0.07
0.07
0.12
0.01
15669 D1
•;;V<:4/1;2/90-:-
5/SO/99
O9ES029
ppbv
4.13
1.74
ND
1.95
0.31
0.10
0.13
0.10
ND
0.05
0.05
0.04
0.01
15669 R1
4/1:2/99
5/20/99
69ES036
ppbv
4.13
1.76
ND
1.97
0.31
0.11
0.13
0.09
ND
0.05
0.06
0.04
0.01
15671 D2
4/12/99
5/20/99
O9ES031
ppbv
3.72
1.51
ND
1.62
0.27
0.08
0.11
0.09
ND
0.05
0.06
'0.04
0.01
15671 R2
4/12/99
5/20/99
O9ES032
ppbv
3.71
1.49
ND
1.60
0.28
0.08
0.11
0.08
ND
0.05
0.06
0.04
0.01
15689
4/18/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15703
4/24/99
5/20/99
O9ES023
ppbv
2.23
0.88
ND
0.92
0.15
0.03
0.07
0.04
ND
0.03
0.01
0.03
ND
u - Concentration is below the detection limit
d - Concentration determined using a
dilution factor
4 of 7
-------
1998 UATMP CARBONYLS
Sample Site: El Paso, TX
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15724D1
5/6/99
6/5/99
Q9FD033
ppbv
2.51
0.72
0.01
1.04
0.12
ND
0.21
0.06
0.03
0.03
0.04
0.02
ND
15724R1
5/6/99
6/5/99
Q9FD034
ppbv
2.63
0.74
0.01
1.09
0.09
ND
0.19
0.06
0.02
0.03
0.04
0.07
ND
15726D2
5/6/99
6/5/99
Q9FD035
ppbv
2.45
0.68
0.01
0.95
0.10
ND
0.18
0.06
0.04
0.03
0.05
0.01
ND
15726 R2
5/6/99
6/5/99
Q9FD036
ppbv
2.47
0.64
0.01
0.92
0.08
ND
0.18
0.04
0.02
0.02
0.04
0.02
ND
15782
5/18/99
6/9/99
Q9FH020
ppbv
3.57
1.19
ND
1.27
0.15
0.02
0.27
0.05
0.03
0.04
0.05
0.02
ND
15814
5/30/99
6/10/99
Q9FH029
ppbv
3.58
1.03
0.01
1.34
0.11
ND
0.20
0.05
0.04
0.04
0.06
0.03
ND
15845
6/11/99
6/19/99
O9FR024
ppbv
3.14
0.82
0.02
1.06
0.10
0.01
0.09
0.07
0.01
0.04
0.07
0.06
ND
15934
6/23/99
7/7/99
O9GF023
ppbv
3.90
1.39
0.02
1.93
0.19
0.01
0.17
0.08
0.01
0.05
0.07
0.04
ND
u - Concentration is below the detection limit
d - Concentration determined using a
dilution factor
-------
1998 UATMP CARBONYLS
Sample Site: El Paso, TX
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15979
7/5/99
8/6/99
09HE017
ppbv
21.09d
6.68d
0.51d
0.51d
0.29d
O.OSd
0.27d
0.63d
ND
0.20d
0.23d
0.27d
O.OSd
16129
7/17/99
8/6/99
O9HE030
ppbv
30.14d
6.79
0.75
0.22
0.30
0.06
0.21
0.65
ND
0.33
0.17
0.24
ND
16197
7/29/99
8/6/99
O9HE038
ppbv
29.15d
6.75
0.66
0.38
0.25
0.06
0.20
0.63
ND
0.24
0.16
0.26
ND
16329
8/10/99
8/25/99
O9HX019
ppbv
7.20
2.47
0.18
0.84
0.11
0.01
0.17
0.17
0.01
. 0.07
0.09
0.07
ND
16445
8/22/99
9/11/99
O9IJ024
ppbv
9.44d
3.04
0.12
1.77
0.28
0.01
0.34
0.18
0.020
0.09
0.10
0.10
ND
16687
9/3/99
9/23/99
O9IV018
ppbv
6.95
2.01
0.12
1.37
0.16
0.01
0.18
0.14
ND
0.05
0.08
0.06
ND
u - Concentration is below the detection limit
d - Concentration determined using a
dilution factor
6 of 7
-------
FIELD BLANK DATA
Sample site: El Paso, TX
RAW AMOUNT
Derivatized Cone. (ug/mL)
Data File ID
FBID
Sample date
Date Analyzed
Q8KK01 1
15002FB
9/20/98
11/11/98
O9CS010
15529FB
3/13/99
3/30/99
O9EK008
15636FB
4/6/99
5/11/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.09
0.36
0.00
0.44
0.00
0.00
0.45
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.03
0.00
0.00
0.00
0.00
0.07
0.00
0.00
0.00
0.00
0.06
0.08
0.00
0.33
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
O9ES008
15704FB
4/24/99
5/19/99
0.08
0.08
0.05
0.15
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
0.00
Q9FH010
15783FB
5/18/99
6/9/99
0.42
0.09
0.00
0.23
0.00
0.00
0.38
0.00
0.00
0.00
0.00
0.04
0.00
Field Blanks
Underivatized Cone, (total ug)
Data File ID
FBID
Date Analyzed
Q8KK01 1
15002FB
11/11/98
O9C$010
15529FB
3/30/99
O9EK008
15636FB
5/11/99
O9ES008
15704 FB
5/19/99
Q9FH010
15783FB
6/9/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.05
0.28
ND
0.42
ND
ND
0.51
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.02
ND
ND
ND
ND
0.10
ND
ND
ND
ND
0.04
0.06
ND
0.32
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.05
0.07
0.05
0.15
ND
ND
ND
ND
ND
ND
ND
ND
ND
0.24
0.07
ND
0.22
ND
ND
0.44
ND
ND
ND
ND
0.05
ND
7 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Garyville, LA
GALA
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
14801
9/2/98
10/28/98
Q8J-018
ppbv
1.69
0.59
0.04
0.48
0.11
ND
0.17
0.09
0.02
0.05
0.02
0.05
0.01
14805
9/14/98
10/30/98
Q8J#021
ppbv
1.84
1.39
0.03
0.25
0.18
ND
0.33
0.04
0.01
0.22
ND
0.08
ND
15099
9/26/98
11/12/98
Q8KK035
ppbv
2.15
1.00
0.04
0.31
0.23
ND
0.40
0.07
0.03
0.24
0.04
0.09
ND
15117
10/8/98
11/16/98
Q8KP019
ppbv
2.15
1.11
0.02
0.69
0.23
ND
0.42
0.07
0.03
0.31
0.02
0.09
ND
15134
10/14/98
11/16/98
Q8KP020
ppbv
3.26
1.39
0.02
0.79
0.27
ND
0.45
0.06
0.03
0.23
0.04
0.09
ND
15172
10/28/98
11/25/98
Q8KW020
ppbv
2.26
1.33
0.03
0.42
0.27
ND
0.48
0.08
0.06
0.27
0.03
0.10
ND
15182
11/7/98
12/22/98
Q8LU022
ppbv
1.71
1.30
0.02
0.86
0.22
ND
0.27
0.08
0.044
0.23
0.04
0.12
ND
15232
11/19/98
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15265
12/1/98
1/8/99
O9AG027
ppbv
1.80
1.36
0.01
0.62
0.25
0.01
0.19
0.04
0.01
0.18
0.03
0.10
ND
u - Concentration is below the detection limit
1 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Garyville, LA
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15257
12/13/98
1/8/99
O9AG030
ppbv
0.88
0.63
0.01
0.65
0.15
0.005
0.14
0.03
0.01
0.15
0.02
0.07
ND
15295
12/25/98
1/8/99
O9AG041
ppbv
0.58
0.50
0.02
0.51
0.11
0.005
0.11
0.03
0.01
0.12
0.02
0.07
0.003
15398 D1
2/5/99
3/16/99
09CO072
ppbv
2.64
1.29
ND
0.50
0.34
0.07
0.18
0.05
0.04
0.29
0.03
0.13
ND
15398R1
2/5/99
3/16/99
09CO073
ppbv
2.63
1.29
ND
0.46
0.32
0.07
0.18
0.05
0.04
0.30
0.03
0.14
ND
15396D2
2/5/99
3/16/99
09CO074
ppbv
2.40
1.22
ND
0.62
0.32
0.07
0.16
0.05
0.04
0.27
0.03
0.11
ND
15396 R2
2/5/99
3/17/99
09CO075
ppbv
2.40
1.22
ND
0.59
0.30
0.08
0.17
0.06
0.040
0.27
0.03
0.11
ND
15412
2/17/99
3/16/99
09CO037
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15460
2/23/99
3/16/99
09C0047
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
u - Concentration is below the detection limit
2, Of 7
-------
1998 UATMP CARBONYLS
Sample Site: Garyville, LA
Derivatized Cone. (ug/mL) ; ,
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15505
3/7/99
3/17/99
oicoioii
ppbv
2.24
1.24
ND
0.76
0.31
0.04
0.21
0.05
0.05
0.37
0.05
0.11
ND
15524
3/13/99
4/1/99
O9C%024
ppbv
1.55
0.70
ND
0.31
0.22
0.02
0.11
0.02
0.04
0.24
0.01
0.07
ND
15561
3/19/99
4/14/99
09DM023
ppbv
2.95
1.21
ND
0.52
0.26
ND
0.12
0.03
ND
0.15
0.02
0.08
ND
15592 PI
3/25/99
4/14/99
O9DM049
ppbv
1.34
0.50
ND
0.51
0.15
ND
0.06
0.02
ND
0.09
0.01
0.04
ND
15592 R1
3/25/99
4/14/99
O9DM050
ppbv
1.35
0.50
ND
0.52
0.15
ND
0.06
0.02
ND
0.09
0.01
0.05
ND
15594D2
3/25/99
4/14/99
O9DM051
ppbv
1.69
0.63
ND
0.48
0.16
ND
0.07
0.02
ND
0.11
0.01
0.07
ND
15594R2
3/25/99
4/14/99
O9DM052
ppbv
1.73
0.64
ND
0.48
0.15
ND
0.07
0.02
ND
0.11
0.01
0.07
ND
15621
3/31/99
5/12/99
09EK021
ppbv
1.67
0.93
0.01
0.35
0.14
0.03
0.09
0.03
ND
0.08
0.001
0.05
ND
u - Concentration is below the detection limit
3 Of 7
-------
1998 UATMP CARBONYLS
Sample Site: Garyville, LA
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Folualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15663D1
4/12/99
5/20/99
O9ES033
ppbv
3.66
0.99
ND
1.04
0.23
0.12
0.11
0.03
ND
0.11
ND
0.06
ND
15663 R1
4/12/99
5/20/99
O9ES034
ppbv
3.67
1.00
ND
1.04
0.17
0.04
0.11
0.03
ND
0.14
ND
0.06
ND
15665D2
4/12/99
5/20/99
O9ES035
ppbv
3.59
0.98
ND
0.64
0.22
0.04
0.10
0.03
ND
0.11
0.00
0.06
ND
15665 R2
4/12/99
5/20/99
O9ES036
ppbv
3.69
0.98
ND
0.64
0.22
0.04
0.10
0.03
ND
0.14
ND
0.06
ND
15691
4/18/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15693D1
4/24/99
6/5/99
Q9FD029
ppbv
2.38
0.80
0.02
0.47
0.19
ND
ND
0.12
ND
0.12
0.10
ND
ND
15693R1
4/24/99
6/5/99
Q9FD030
ppbv
2.48
0.81
0.03
0.49
0.21
ND
ND
0.12
ND
0.12
0.05
ND
ND
15694D2
4/24/99
6/5/99
Q9FD031
ppbv
2.26
0.80
0.02
0.32
0.19
ND
ND
0.11
ND
0.10
0.05
ND
ND
u - Concentration is below the detection limit
4 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Garyville, LA
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15694R2
4/24/99
6/5/99
Q9FD032
ppbv
2.22
0.76
0.01
0.32
0.19
ND
ND
0.12
ND
0.10
0.05
ND
ND
15741
4/30/99
6/5/99
Q9FD019
ppbv
3.25
1.00
0.01
0.96
0.24
ND
ND
0.09
ND
0.20
0.04
ND
ND
15753
5/6/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15755
5/6/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15777
5/12/99
6/9/99
Q9FH017
ppbv
2.10
0.80
0.02
0.32
0.17
ND
0.38
0.08
0.055
0.07
. 0.05
0.04
ND
15767D1
5/18/99
6/10/99
Q9FH040
ppbv
4.54
1.21
0.04
0.80
0.24
ND
0.52
0.12
0.038
0.16
0.07
0.08
ND
15767R1
5/18/99
6/10/99
Q9FH041
ppbv
4.56
1.25
0.04
0.82
0.23
ND
0.47
0.05
0.075
0.12
0.06
0.08
ND
15768D2
:'$M$&Si
6/10/99":;;
' Q9FH042;^:
ppbv
4.76
1.23
0.04
0.48
0.26
ND
0.44
0.10
0.035
0.16
0.05
0.08
ND
u - Concentration is below the detection limit
5 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Garyville, LA
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/Isobutyraldehyde
Benzaldehyde
sovaleraldehyde
Valeraldehyde
Folualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15768R2
5/18/99
6/10/99
Q9FH043
ppbv
4.65
1.25
0.02
0.46
0.25
ND
0.40
0.10
0.086
0.17
0.03
0.06
ND
15818
5/30/99
6/10/99
Q9FH030
ppbv
2.21
1.17
0.04
0.38
0.33
0.12.
0.42
0.07
0.026
0.16
0.07
0.07
0.01
15857
6/11/99
6/18/99
O9FR019
ppbv
2.18
1.06
ND
0.42
0.27
ND
0.25
0.12
0.02
0.21
0.05
0.10
ND
15986
7/5/99
8/6/99
O9HE018
ppbv
1.91
0.77
ND
0.29
0.25
ND
0.19
0.06
0.02
0.23
0.05
0.13
ND
16058
7/17/99
8/6/99
O9HE040
ppbv
3.22
1.93
ND
0.29
0.29
ND
0.23
0.10
0.02
0.21
0.05
0.14
ND
16206
7/29/99
8/6/99
O9HE039
ppbv
4.57
1.71
ND
0.38
0.44
ND
0.31
0.18
0.02
0.34
0.07
0.18
ND
16350
8/10/99
8/25/99
O9HX020
ppbv
2.37
1.26
ND
0.49
0.38
ND
0.30
0.09
0.02
0.30
0.07
0.15
ND
16684
9/3/99
9/23/99
09IV017
ppbv
1.84
1.03
ND
0.31
0.34
ND
0.19
0.06
ND
0.22
0.03
0.16
ND
u - Concentration is below the detection limit
6.Qf7
-------
FIELD BLANK DATA
Sample site: Garyviile, LA
RAW AMOUNT
Derivatized Cone. (ug/mL)
Data File ID
FBID
Sample date
Date Analyzed
Q8KK013
15100FB
9/26/98
11/11/98
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.04
0.31
0.00
0.45
0.02
0.00
0.51
0.04
0.00
0.02
0.00
0.04
0.00
Field Blanks
Underivatized Conc.(total ug)
Data File ID
FBID
Date Analyzed
Q8KK013
15100FB
11/11/98
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.02
0.24
ND
0.44
0.02
ND
0.58
0.06
ND
0.03
ND
0.06
ND
7 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Hahnville, LA
HALA
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15105
9/14/98
10/30/98
Q8J#022
ppbv
1.05
0.30
0.01
0.18
0.05
ND
0.10
0.02
0.03
0.03
ND
0.06
ND
15102
9/26/98
11/12/98
Q8KK036
ppbv
1.97
0.41
0.02
0.17
0.10
ND
0.25
0.03
0.04
0.04
ND
0.06
ND
15132
10/14/98
11/17/98
Q8KP022
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15170
10/26/98
11/25/98
Q8KW017
ppbv
4.04
1.04
0.03
1.37
0.14
ND
0.40
0.06
0.08
0.05
0.03
0.07
ND
15180
11/7/98
12/22/98
Q8LU024
ppbv
2.09
1.12
0.04
1.27
0.15
ND
0.24
0.05
0.06
0.05
0.06
0.05
ND
15224
11/19/98
12/22/98
Q8LU031
ppbv
5.04
1.38
0.19
0.77
0.25
ND
0.20
0.04
0.12
0.06
0.06
0.06
0.02
15222
12/1/98
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15255
12/13/98
1/8/99
O9AG032
ppbv
0.83
0.48
0.02
0.90
0.06
0.003
0.16
0.02
0.002
0.04
0.02
0.03
0.002
u - Concentration is below the detection limit
1j2f7
-------
1998 UATMP CARBONYLS
Sample Site: Hahnville, LA
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15293
12/25/98
1/8/99
O9AG043
ppbv
0.74
0.37
0.01
0.70
0.06
0.004
0.29
0.02
0.01
0.04
0.02
0.03
ND
15315
1/9/99
2/20/99
O9BS021
ppbv
1.03
0.67
0.005
1.02
0.11
0.01
0.15
0.02
ND
0.14
0.01
0.04
ND
15392D1
2/5/99
3/16/99
09CO068
ppbv
2.71
1.12
ND
0.88
0.32
0.13
0.11
0.06
0.02
0.23
0.02
0.06
ND
15392R1
2/5/99
3/16/99
09CO069
ppbv
2.68
1.10
ND
0.86
0.31
0.13
0.11
0.08
0.03
0.26
0.03
0.07
ND
15394D2
2/5/99
3/16/99
09CO070
ppbv
2.59
1.08
ND
0.83
0.31
0.12
0.11
0.08
ND
0.25
0.03
0.06
ND
15394R2
2/5/99
3/16/99
09CO071
ppbv
2.56
1.03
ND
0.83
0.31
0.11
0.10
0.06
ND
0.24
0.03
0.07
ND
15416
2/13/99
VOID
09CO050
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15458
2/23/99
3/16/99
09CO050
ppbv
1.43
0.80
ND
1.13
0.20
0.06
0.10
0.04
0.03
0.21
0.05
0.05
ND
u - Concentration is below the detection limit
2 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Hahnville, LA
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15494
3/1/99
3/17/99
O9CQ014
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15492
3/7/99
3/17/99
O9CQ016
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15557D1
3/19/99
6/5/99
Q9FD042
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15559 D2
3/19/99
6/5/99
Q9FD044
ppbv
3.10
1.44
0.02
1.43
0.19
ND
0.58
0.06
ND
0.14
0.04
0.08
ND
15596
3/25/99
4/14/99
O9DM029
ppbv
0.03
0.04
ND
0.09
0.01
ND
0.01
ND
ND
ND
0.003
ND
ND
15619
3/31/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15681
4/6/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15659D1
4/18/99
5/20/99
09ES042
ppbv
1.49
1.05
ND
1.19
0.19
0.07
0.07
0.02
ND
0.05
0.01
0.06
0.00
u - Concentration is below the detection limit
3nf7
-------
1998 UATMP CARBONYLS
Sample Site: Hahnville, LA
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15659 R1
4/18/99
5/20/99
O9ES043
ppbv
1.50
1.04
ND
1.19
0.19
0.07
0.08
0.02
ND
0.04
0.00
0.05
ND
15661 D2
4/18/99
5/20/99
O9ES044
ppbv
1.75
1.13
ND
1.27
0.20
0.07
0.08
0.02
ND
0.05
0.01
0.06
ND
15661 R2
4/18/99
5/20/99
O9ES045
ppbv
1.74
1.12
ND
1.26
0.20
0.08
0.08
0.02
ND
0.05
0.01
0.06
ND
15738 01
4/30/99
6/5/99
Q9FD038
ppbv
1.70
0.54
0.01
1.22
0.06
ND
ND
ND
ND
ND
0.04
0.02
ND
15738R1
4/30/99
6/5/99
Q9FD039
ppbv
1.68
0.52
0.01
1.20
0.06
ND
ND
ND
ND
ND
0.03
' 0.02
ND
15739D2
4/30/99
6/5/99
Q9FD040
ppbv
1.92
0.55
0.01
1.17
0.06
ND
ND
ND
ND
0.03
0.04
0.02
ND
15739R2
4/30/99
6/5/99
Q9FD041
ppbv
1.85
0.55
0.01
1.13
0.05
ND
ND
ND
ND
0.02
0.02
0.02
ND
15763
5/6/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
u - Concentration is below the detection limit
4 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Hahnville, LA
Derivatized Cone. (ug/mLj
sWpLEbATE
ANALYSIS DATE
FILENAME '" / •' '.::": :V:-V-': •: '
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15765
5/6/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15770
5/18/99
6/9/99
Q9FH021
ppbv
2.99
1.33
0.05
0.49
0.18
ND
0.16
0.06
0.03
0.09
0.04
0.06
ND
15820D1
5/30/99
6/11/99
Q9FK004
ppbv
1.24
0.53
0.01
0.29
0.09
ND
0.23
0.05
0.03
0.03
ND
0.04
ND
15820R1
5/30/99
6/11/99
Q9FK005
ppbv
1.29
0.55
0.02
0.28
0.08
ND
0.23
0.04
ND
0.03
ND
0.04
ND
15821 D2
5/30/99
6/11/99
Q9FK006
ppbv
1.34
0.60
0.02
0.28
0.10
ND
0.23
0.03
0.02
0.02
0.03
0.04
ND
15821 R2
5/30/99
6/11/99
Q9FK007
ppbv
1.35
0.58
0.01
0.28
0.09
ND
0.25
0.03
0.03
0.03
0.03
0.04
ND
15855
6/11/99
6/18/99
09FR020
ppbv
1.33
0.56
ND
0.48
0.12
ND
0.10
0.06
0.01
0.05
0.03
0.07
ND
15984
7/5/99
8/6/99
O9HE019
ppbv
1.17
0.38
ND
0.03
0.06
ND
0.05
0.03
0.01
0.02
0.01
0.04
ND
u - Concentration is below the detection limit
-------
1998 UATMP CARBONYLS
Sample Site: Hahnville, LA
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
16061
7/17/99
8/6/99
O9HE031
ppbv
1.01
0.40
0.00
0.03
0.05
ND
ND
0.01
ND
0.03
ND
0.04
ND
16202
7/29/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
16348
8/10/99
8/25/99
O9HX021
ppbv
0.93
0.17
ND
0.06
0.04
ND
ND
0.02
0.01
0.03
0.02
0.03 '
ND
16449
8/22/99
9/11/99
09IJ025
ppbv
1.02
0.36
0.01
0.04
0.05
ND
0.17
0.02
0.01
0.03
0.01
0.02
ND
16678
9/3/99
9/23/99
O9IV016
ppbv
0.61
0.33
0.01
0.04
0.03
ND
0.03
0.01
0.01
0.01
ND
0.03
ND
u - Concentration is below the detection limit
6 of 7
-------
FIELD BLANK DATA
Sample site: Hahnville, LA
RAW AMOUNT
Derivatized Cone. (ug/mL)
Data File ID
FBID
Sample date
Date Analyzed
Q8KK014
15103 FB
9/26/98
11/11/98
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.11
0.17
0.03
0.44
0.00
0.00
0.68
0.00
0.00
0.04
0.00
0.05
0.00
Field Blanks
Underivatized Cone.(total ug)
Data File ID
FBID
Date Analyzed
Q8KK014
15103FB
11/11/98
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.06
0.14
0.02
0.43
ND
ND
0.77
ND
ND
0.05
ND
0.07
ND
7 of 7
-------
1998 UATMP CARBONYLS
Sample Site: N. Little Rock, AK
PARR
Derivatized Cone. (ug/mL) •••'•..''..
SAMPLE DATE
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
14683
9/3/!98
10/28/98
Q8J^b22
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
14699
0/P$
10/28/98
Q8J-026
ppbv
5.04
1.22
0.04
1.85
0.12
ND
0.43
0.21
0.02
0.02
0.12
0.04
ND
14966;
i 9/20/98 :
ti/12798
<38kko4i
ppbv
1.94
0.75
0.10
0.51
0.11
ND
0.14
0.04
0.03
0.06
0.05
0.07
0.03
15125
10/14/98
11/17/98
Q8KP023
ppbv
2.74
1.14
0.04
2.18
0.15
ND
0.64
0.09
0.01
0.05
0.04
0.03
ND
15146
1,0/26/98
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
•VOID
VOID
15186
11/7/98
12/22/98
Q8LU025 :
ppbv
1.51
1.02
0.02
1.57
0.09
ND
0.20
0.05
0.04
0.03
0.04
0.01
ND
15210
11/19/98
12/22/98
Q8LU032
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15242
12/1/98
12/22/98
Q8LU039
ppbv
1.20
0.65
0.02
1.20
0.06
ND
0.21
0.04
0.04
0.03
0.03
0.02
ND
u - Concentration is below the detection limit
1 of 4
-------
1998 UATMP CARBONYLS
Sample Site: N. Little Rock, AK
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSISiPATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15261
12/13/98
1/8/99 ;
09Aidi033
ppbv
0.75
0.47
0.01
0.83
0.06
ND
0.10
0.02
0.01
0.01
0.01
0.02
ND
1 5279
12/25798
178/99
O9AG044
ppbv
1.60
1.24
0.04
1.00
0.12
0.01
0.13
0.04
0.01
0.02
0.02
0.04
ND
15325
1/6/99
2/20/99
O9BS024
ppbv
2.34
1.19
0.02
1.58
0.13
0.01
0.14
0.04
0.01
0.03
0.03
0.04
ND
15363:
1/18/99
2/20/99
O9BS025
ppbv
1.26
0.70
0.02
1.25
0.10
0.004
0.09
0.04
0.01
0.03
0.03
0.03
ND
15373
1/30/$9
3/16/99
09CO025
ppbv :
1.26
0.49
ND
0.78
0.08
ND
0.04
0.04
ND
ND
0.03
0.02
ND
15400
2/11/99
3/16/99
0906630
ppbv
1.01
0.43
ND
0.46
0.08
0.03
0.03
0.02
ND
ND
0.03
0.03
ND
15432
2/1*/99
$/16/$9
09Cd041
ppbv
1.36
0.62
ND
1.28
0.11
0.08
0.04
0.05
ND
0.03
0.04
0.04
ND
15462 i
2/23/99 -
3/16/99
09Cd048
: ppbv
1.83
0.79
ND
1.38
0.14
0.09
0.05
0.05
ND
0.04
0.04
0.02
ND
u - Concentration is below the detection limit
-------
1998 UATMP CARBONYLS
Sample Site: N. Little Rock, AK
Derivatized Cone. (ug/mL) :
S^MPLEbATE '->.r-:;: : ••'•;' ••'' '"'' ' .
ANALysis PATE
PILE NAME • .':;;•'•-, '•;.' .:.• - ''
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15514
3/1/99
3/17/99
09CQ018
ppbv
2.99
1.34
ND
2.02
0.24
0.14
0.09
0.07
ND
0.06
0.05
0.05
ND
15506
3/7/99
3/17/99
O9CQ017
ppbv
1.09
0.52
ND
0.87
0.09
0.04
0.05
0.01
ND
ND
0.02
0.02
ND
15598 O1
3/17/99
4/14/99
09DM035
ppbv
1.55
0.68
ND
1.25
0.11
ND
0.04
0.03
ND
0.02
0.02
0.03
ND
15598R1
3/17/99
4/14/99
O9DM037
ppbv
1.57
0.68
ND
1.26
0.11
ND
0.04
0.03
ND
0.01
0.02
0.02
ND
15600 02
3/17/99
4/14/99
O9DM038
ppbv
1.54
0.67
ND
1.25
0.11
ND
0.04
0.03
ND
0.02
0.02
0.02
ND
15600R2
3/17/99
4/14/99
09DM039
ppbv
1.59
0.67
ND
1.26
0.11
ND
0.04
0.03
ND
0.02
0.02
0.02
ND
15585
3/25/99
4/14/99
O9DM028
ppbv
1.39
0.69
ND
1.28
0.12
ND
0.05
0.02
ND
0.02
0.01
0.03
ND
15615
3/31/99
5/12/99
O9EK023
ppbv
1.50
0.70
ND
0.82
0.12
0.06
0.06
0.04
ND
0.02
0.00
0.03
ND
u - Concentration is below the detection limit
3 of 4
-------
FIELD BLANK DATA
Sample site: N. Little Rock, AR
RAW AMOUNT
Derivatized Cone. (ug/mL)
Data File ID
FBID
Sample date
Date Analyzed
Q8KK012
14967FB
9/21/98
11/11/98
O9DM010
15586FB
3/25/99
4/13/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.10
0.07
0.00
0.37
0.00
0.00
0.61
0.00
0.00
0.00
0.00
0.03
0.00
0.14
0.06
0.00
0.13
0.02
0.00
0.00
0.00
0.00
0.00
0.02
0.00
0.00
Field Blanks
Underivatized Conc.(total ug)
Data File ID
FBID
Date Analyzed
Q8KK012
14967FB
11/11/98
O9DM010
15586FB
4/13/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.06
0.06
ND
0.36
ND
ND
0.70.
ND
ND
ND
ND
0.05
ND
0.08
0.05
ND
0.12
0.02
ND
ND
ND
ND
ND
0.03
ND
ND
4 of 4
-------
1998 UATMP CARBONYLS
Sample Site: Rutland, VT
RUVT
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
14691
9/2/98
10/28/98
Q8J-020
ppbv
2.18
0.93
0.04
ND
1.36
ND
0.39
0.06
0.01
0.03
ND
0.04
ND
14822
9/14/98
10/30/98
Q8J#023
ppbv
1.47
0.86
0.14
0.83
0.11
ND
0.11
0.06
0.02
0.03
0.03
0.05
ND
15061
9/26/98
11/12/98
Q8KK042
ppbv
1.70
1.07
0.15
1.18
0.15
ND
0.15
0.05
0.03
0.05
0.04
0.06
0.02
15112
10/8/98
11/17/98
Q8KP024
ppbv
1.53
1.06
0.05
1.04
0.14
ND
0.44
0.05
0.03
0.04
0.04
0.03
ND
15136
10/20/98
11/17/98
Q8KP025
ppbv
1.60
0.77
0.01
1.46
0.08
ND
0.41
0.03
ND
0.02
ND
0.02
ND
15158
11/1/98
11/25/98
Q8KW023
ppbv
1.13
0.63
0.02
0.94
0.06
ND
0.33
0.03
ND
0.02
ND
0.01
ND
15202
11/13/98
11/25/98
Q8KW028
ppbv
1.75
0.83
0.03
1.27
0.09
ND
0.21
0.05
0.020
0.02
0.04
0.02
0.01
15230
11/25/98
12/21/98
Q8LU012
ppbv
1.44
0.77
0.02
1.00
0.07
ND
0.16
0.05
0.02
0.02
0.03
0.02
0.02
u - Concentration is below the detection limit
1 of 6
-------
1998 UATMP CARBONYLS
Sample Site: Rutland, VT
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15246
12/7/98
12/22/98
Q8LU017
ppbv
1.36
0.62
0.01
0.99
0.07
ND
0.12
0.03
ND
0.02
0.03
0.02
0.01
15281
12/19/98
1/8/99
O9AG036
ppbv
2.13
1.47
0.07
1.35
0.17
0.02
0.19
0.09
0.02
0.03
0.08
0.04
ND
15307
12/31/98
2/20/99
O9BS018
ppbv
2.02
1.29
0.06
1.08
0.13
0.02
0.14
0.08
0.01
0.03
0.07
0.03
ND
15321
1/12/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15346 D1
1/24/99
2/20/99
O9BS035
ppbv
1.08
0.80
0.01
0.96
0.09
0.01
0.08
0.05
0.01
0.02
0.04
0.05
ND
15346 R1
1/24/99
2/20/99
O9BS036
ppbv
1.11
0.80
0.01
0.95
0.08
0.01
0.08
0.05
0.01
0.02
0.04
0.05
0.00
15348D2
1/24/99
2/20/99
O9BS038
ppbv
1.11
0.80
0.01
0.94
0.09
0.01
0.08
0.05
0.01
0.02
0.04
0.04
ND
15348 R2
1/24/99
2/20/99
O9BS039
ppbv
1.13
0.81
0.01
0.96
0.09
0.01
0.09
0.05
0.01
0.02
0.04
0.04
ND
u - Concentration is below the detection limit
-------
1998 UATMP CARBONYLS
Sample Site: Rutland, VT
Derivatized I C0nC- (ucj/rnk)
sAMPiJE bATE •'.; • ':' '••'• :
ANALMjSDATE
FILENAME
UNITS ;
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15410
2/5/99
3/16/99
09CO027
ppbv
1.10
0.59
ND
0.72
0.10
0.04
0.04
0.02
ND
0.03
0.02
0.01
ND
15446
2/17/99
3/16/99
09CO038
ppbv
1.91
0.98
ND
1.25
0.16
0.10
0.06
0.05
ND
0.03
0.04
0.04
ND
15480
3/1/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15551
3/13/99
4/1/99
O9C%025
ppbv
1.32
0.66
ND
0.76
0.11
0.04
0.04
0.02
ND
0.02
0.01
0.005
ND
15567
3/19/99
4/14/99
O9DM024
ppbv
1.44
0.68
ND
0.65
0.10
ND
0.04
0.01
ND
0.01
0.01
0.01
ND
15629 D1
3/25/99
5/12/99
O9EK042
ppbv
1.46
0.58
0.02
0.81
0.09
0.02
0.04
0.01
ND
0.01
ND
0.01
ND
15629R1
3/25/99
5/12/99
O9EK043
ppbv
1.48
0.58
0.02
0.81
0.09
0.02
0.04
0.01
ND
0.01
ND
0.01
ND
15631 D2
3/25/99
5/12/99
O9EK044
ppbv
1.55
0.58
0.02
0.82
0.09
0.02
0.04
0.02
ND
0.01
0.00
0.01
ND
u - Concentration is below the detection limit
3 of 6
-------
1998 UATMP CARBONYLS
Sample Site: Rutland, VT
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15631 R2
3/25/99
5/12/99
O9EK045
ppbv
1.59
0.59
0.02
0.82
0.09
0.02
0.04
0.02
ND
0.01
ND
0.01
ND
15633
4/6/99
5/19/99
09ES013
ppbv
2.19
1.11
ND
1.41
0.17
0.07
0.09
0.05
ND
0.03
0.01
0.03
ND
15679
4/18/99
5/19/99
O9ES018
ppbv
0.64
0.30
ND
0.46
0.05
0.02
0.02
0.01
ND
0.01
ND
0.01
ND
15732
4/30/99
6/5/99
Q9FD020
ppbv
3.20
1.65
0.02
2.23
0.19
ND
0.48
0.08
0.013
0.07
0.06
0.11
ND
15823
5/12/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15825
5/12/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15785
5/24/99
6/10/99
Q9FH025
PPbV
2.25
0.85
0.03
1.22
0.11
ND
0.34
0.06
ND
0.04
0.04
0.03
ND
15905
6/5/99
7/6/99
O9GF014
ppbv
3.56
1.50
ND
2.31
0.23
ND
0.33
0.15
0.03
0.06
0.05
0.08
0.01
u - Concentration is below the detection limit
4 of 6
-------
1998 UATMP CARBONYLS
Sample Site: Rutland, VT
Deri vat ized Gone. (ug/mL)
§AJMPLlbAtE '•'''• " : ; ,
ANALYSisldAtE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15926
6/17/99
VOID
voilp
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
16027
6/29/99
W?9
pgriEoti
ppby
3.35
1.10
ND
0.20
0.20
ND
0.21
0.09
0.02
0.07
0.05
0.09
0.01
16259
7/17/99
8/19/99
O9H
-------
FIELD BLANK DATA
Sample site: Rutland, VT
RAW AMOUNT
Derivatized Cone. (ug/mL)
Data File ID
FBID
Sample date
Date Analyzed
Q8J#009
14823FB
9/14/98
10/29/98
O9C%011
15552FB
3/13/99
3/30/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.03
0.05
0.00
0.35
0.00
0.00
0.37
0.00
0.00
0.00
0.00
0.00
0.00
0.05
0.08
0.00
0.16
0.00
0.00
0.00
0.00
0.00
0.00
0.02
0.00
0.00
Field Blanks
Underivatized Conc.(total ug)
Data File ID
FBID
Date Analyzed
Q8J#009
14823FB
10/29/98
O9C%011
15552FB
3/30/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.02
0.04
ND
0.34
ND
ND
0.43
ND
ND
ND
ND
ND
ND
0.03
0.06
ND
0.16
ND
ND
ND
ND
ND
ND
0.04
ND
ND
6 of 6
-------
1998 UATMP CARBONYLS
Sample Site: Texarkana, AK
GREY
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
14557
9/1/98
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
14696
9/5/98
10/28/98
Q8J-027
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
14887
9/17/98
10/30/98
Q8J#028
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15119
10/14/98
11/17/98
Q8KP021
ppbv
4.18
1.21
0.03
1.16
0.10
ND
0.41
0.06
0.01
0.07
0.04
0.15
ND
15142
10/25/98
11/25/98
Q8KW013
ppbv
VOID
VOID
(VOID
VOID
;VOID
,VOID
(
;VOID
[VOID
VOID
VOID
VOID
VOID
VOID
15174
11/7/98
12/22/98
Q8LU023
ppbv
1.49
0.82
0.01
0.89
0.08
ND
0.14
0.03
0.02
0.02
0.03
0.02
ND
15220
11/13/98
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15240
12/3/98
12/22/98
Q8LU038
ppbv
1.93
0.39
0.03
1.35
0.04
ND
0.21
0.04
0.03
0.01
0.05
0.03
ND
u - Concentration is below the detection limit
d - Concentration determined using a
dilution factor
1 of 4
-------
1998 UATMP CARBONYLS
Sample Site: Texarkana, AK
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15259
12/13/98
1/8/99
O9AG031
ppbv
0.50
0.31
0.002U
0.86
0.03
ND
0.11
0.05
ND
0.02
0.03
0.07
ND
15287
12/25/98
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15313
1/6/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
15365
1/18/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
t15371
1/30/99
VOID
VOID
ppbv
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
"VOID
VOID
15420
2/11/99
3/16/99
09CO031
ppbv
2.24
0.99
ND
0.55
ND
0.07
0.05
0.05
ND
0.05
0.03
0.04
ND
15440
2/23/99
3/16/99
09CO044
ppbv
1.11
0.63
ND
1.26
0.09
0.04
0.03
0.02
ND
0.03
0.02
0.03
ND
15488
3/7/99
3/17/99
O9CQ012
ppbv
2.04
0.91
ND
1.38
0.14
0.05
0.05
0.03
ND
ND
0.03
0.03
ND
u - Concentration is below the detection limit
d - Concentration determined using a
dilution factor
2 of 4
-------
1998 UATMP CARBONYLS
Sample Site: Texarkana, AK
Derivatized Cone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
rolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15508
; 3/13/99
3/17/99
O9CIQ013
ppbv
1.37
0.65
ND
0.65
0.10
0.05
0.04
0.03
ND
0.03
0.02
0.03
ND
15531
3/19/99
4/1/99
09C%029
ppbv
2.02
0.92
ND
1.23
0.22
0.04
0.05
0.03
ND
0.05
0.02
0.03
ND
15565
3/25/99
5/12/99
O9EK018
ppbv
0.38
0.35
, 0.01
, 0.41
0.03
0.01
0.02
0.01
ND
0.004
ND
0.01
ND
15623
3/31/99
5/12/99
09Ek022
ppbv
0.76
0.49
ND
0.74
0.05
0.02
0.03
0.01
ND
0.01
ND
0.02
ND
u - Concentration is below the detection limit
d - Concentration determined using a
dilution factor
3 of 4
-------
FIELD BLANK DATA
Sample site: GREY
RAW AMOUNT
Derivatized Cone. (ug/mL)
Data File ID
FBID
Sample date
Date Analyzed
Q8J-007
14558FB
9/1/98
10/27/98
Q8J#01 1
14888FB
9/17/98
10/29/98
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
Q8KP007
15097FB
10/6/98
11/16/98
15.46
2.32
0.13
2.36
0.19
0.00
0.96
0.25
0.05
0.39
0.00
1.58
0.12
Field Blanks
Underivatized Cone.(total ug)
Data File ID
FBID
Date Analyzed
Q8J-007
14558FB
10/27/98
Q8J#01 1
14888 FB
10/29/98
Q8KP007
15097FB
11/16/98
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
8.84
1.82
0.12
2.30
0.18
ND
1.10
0.37
0.07
0.51
ND
2.25
0.21
44
-------
1998 UATMP CARBONYLS
Sample Site: Underbill, VT
UNVT
Derivatized Cone. (ug/mL)
SAMPLEiDATE
/ANALYSIS DATE
fiLEWAWiE : •:." . : •• ...: ": .
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
14681
9/2/98
10/28/98
Q8J~02i
ppbv
0.84
0.32
0.03
0.56
0.04
ND
0.04
0.01
0.01
0.01
ND
0.01
0.01
14816
9/14/9$
10/30/98 i
Q8J#024
: ;ppbv
0.57
0.33
0.07
0.55
0.03
ND
0.04
0.02
ND
0.01
ND
0.01
ND
15053
9/26/98
11/12/98
Q8KK043
ppbv
1.06
0.71
0.11
1.07
0.08
ND
0.09
0.04
0.01
0.02
ND
0.02
0.02
15110
10/8/98
11/17/98
Q8KP027
ppbv
0.70
0.50
ND
0.84
0.06
ND
0.48
0.02
ND
0.02
ND
0.02
ND
15140
10/20/98
11/17/98
Q8KP028
ppbv
0.70
0.39
ND
1.14
0.05
ND
0.31
0.02
ND
0.01
ND
0.01
ND
15160
11/1/98
11/25/98
Q8KW024
ppbv
0.52
0.28
0.01
0.72
0.04
ND
0.29
0.03
0.01
0.01
0.02
0.02
ND
15200
11/13/98
11/25/98
Q8KW029
ppbv
0.45
0.30
0.01
0.80
0.03
ND
0.15
0.02
ND
0.01
ND
ND
ND
15226
11/25/98
12/21/98
Q8LU013
ppbv
0.46
0.29
0.01
0.69
0.03
0.01
0.08
0.02
0.01
0.01
0.01
0.01
ND
u - Concentration is below the detection limit
1 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Underbill, VT
Derivatized Gone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NARflE
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15248
12/7/98
12/22/98
Q8LU018
PpbV :
0.65
0.33
0.01
0.80
0.04
ND
0.08
0.02
0.01
0.01
0.02
0.02
0.01
15289
12/19/98
1/8/99
O9AG038
ppbv
0.63
0.46
0.01
0.70
0.06
0.003
0.08
0.02
ND
0.01
0.01
0.02
0.01
15309
12/31/98
2/20/99
O9BS019
ppbv
0.58
0.39
0.01
0.55
0.04
ND
0.04
0.02
ND
0.01
0.01
0.02
ND
15323
1/12/99
2/20/99
0985023
ppbv
0.87
0.72
0.01
0.90
0.08
0.004
0.08
0.02
ND
0.02
0.01
0.02
ND
15359D1
1/24/99
2/20/99
O9BSd40
ppbv
0.51
0.29
0.0007U
0.55
0.04
ND
0.03
0.01
ND
0.01
ND
0.02
ND
15359 ;.R1.
1/24/99
2/20/99
O9BS041
ppbv
0.52
0.29
O.OOOSu
0.54
0.04
ND
0.03
0.01
ND
0.01
ND
0.02
ND
15361 D2;
: 1/24/99 ;
2/20/99
O9BS042
ppbv
0.54
0.34
0.0006U
0.61
0.04
ND
0.05
0.01
ND
0.01
ND
0.02
ND
15361 R2
1/24/99
2/20/99
O9BS043
ppbv;
0.56
0.34
O.OOOSu
0.61
0.04
ND
0.04
0.01
ND
0.01
ND
0.02
ND
u - Concentration is below the detection limit
2 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Underbill, VT
Derivatized Cone. (Ug/mL)
SAMPLE DATE
ANALYSIS DATE
FILE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15418
2/5/99
3/16/99
09CC>029
ppbv
0.50
0.30
ND
0.59
0.05
0.02
0.02
0.01
ND
ND
0.01
0.01
ND
15448
2/17/99
3/1;6/M
O9cdb4o
ppbv
1.20
0.63
ND
0.97
0.10
0.04
0.04
0.02
ND
0.02
0.01
0.01
ND
15486
3/1/99
3/16>99
09GC)053
ppby
0.87
0.36
ND
0.79
0.07
0.02
0.02
0.01
ND
ND
0.02
ND
ND
15545
3/13/99
4/1/99
d9C6/od27
ppbv
0.85
0.44
ND
0.67
0.07
0.03
0.02
0.01
ND
0.01
0.01
0.01
ND
15569
3/19/99;
4/14/99
09bMb26
ppbv
0.55
0.24
ND
0.49
0.04
ND
0.01
0.003
ND
0.003
0.01
0.01
ND
15581 D1
3/25/9$ :
4/14/99
09DM053
ppbv
0.45
0.23
ND
0.60
0.04
ND
0.01
0.004
ND
0.002
0.01
0.01
ND
15581 R1
3/25/9J3 !
4/f4/99
69Mto54
ppbv
0.46
0.23
ND
0.59
0.04
ND
0.01
0.004
ND
ND
0.01
0.01
ND
u - Concentration is below the detection limit
3 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Underbill, VT
Derivatized Gone. (ug/mL)
SAMPLE DATE
ANALYSIS DATE
FiLENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15583D2
3/25/99
4/14/99
O9DM055
ppbv
0.52
0.26
ND
0.69
0.04
ND
0.01
0.003
ND
0.001
0.01
0.01
ND
15583R2
3/215/99
4/14/99
O9DM056
ppbv
0.51
0.26
ND
0.69
0.04
ND
0.01
0.005
ND
0.001
0.01
0.01
ND
15643
4/6/99
:5/19/99
69ES015
ppbv
1.11
0.52
0.02
0.97
0.07
0.03
0.03
0.01
ND
0.01
ND
0.01
ND
15667
4/12/99
5/19/99
09ES019
ppbv
0.78
0.33
ND
0.80
0.04
0.02
0.02
0.01
ND
0.01
ND
0.01
ND
15736 :
4/36/99
6/5/99 L;
Q9Fdb21
ppbv
1.42
0.63
0.01
1.34
0.06
ND
0.26
0.03
ND
0.03
0.04
0.04
ND
15800D1
:/:^/i27$9';::.-
6/16/99
d9FH644
ppbv
1.10
0.49
ND
1.36
0.07
ND
0.26
0.03
0.03
0.02
0.04
0.05
ND
15800R1
5/12/99
6/10/99
Q9FH045
ppbv
1.07
0.52
ND
1.35
0.06
ND
0.25
0.03
0.03
0.02
0.05
0.02
ND
15802:02
5/12/99
6/11/99
d9FK662
ppbv
1.25
0.50
ND
1.39
0.06
ND
0.21
0.07
ND
0.02
0.03
0.03
ND
u - Concentration is below the detection limit
-------
1998 UATMP CARBONYLS
Sample Site: Underbill, VT
Deri vatized Cone. (ug/mL);
SAMPLE DATE :
ANALYSIS DATE
FILENAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
15802R2
5/12/99
6/11/99
Q9FK003
ppbv
1.21
0.49
ND
1.33
0.06
ND
0.27
0.03
ND
0.02
0.05
0.04
ND
15792
5/24/99
6/10/99
Q9FH026
ppbv
1.26
0.42
0.01
1.02
0.06
ND
0.34
0.02
ND
0.02
0.04
0.03
ND
15831
6/5/99
6/18/99
O9FR017
ppbv
2.15
0.62
ND
1.90
0.08
ND
0.12
0.05
ND
0.02
0.04
0.02
0.00
15924
6/1 7/99
7/7/99
O9GFOi9
ppbv
1.69
0.50
0.02
1.56
0.08
ND
0.08
0.04
0.01
0.02
0.03
0.03
ND
16029
6729/99
! 8/6/99
O9HE012
ppbv
1.57
0.57
ND
0.26
0.08
ND
0.12
0.05
0.01
0.03
0.03
0.04
ND
16266
:V;::7/l7/99
8/19/99
d9Hd029
ppbv
3.18
0.80
0.02
1.39
0.12
ND
0.12
0.12
0.01
0.04
0.04
0.04
ND
16256
;:H 7/23/99;;
: 8/19/99:
O9HQ033
PpbV ;
2.96
0.81
ND
1.04
0.11
ND
0.11
ND
0.02
0.04
0.04
0.06
ND
16274 :
•I :8/4/99 :
8/25/99 ;
09HX025
ppbv
1.08
0.45
ND
0.92
0.05
ND
0.08
0.05
0.01
0.02
0.04
0.02
ND
u - Concentration is below the detection limit
5 of 7
-------
1998 UATMP CARBONYLS
Sample Site: Underbill, VT
Derivatized Gone. (ug/rhL)
SAiViF>irE:lSAlrE
ANALYSis PATE
RLE NAME
UNITS
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
rolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
16492
8/16/99
9/11/99
09IJ019
ppbv
1.61
0.42
0.01
0.86
0.06
ND
0.07
0.04
0.01
0.02
0.03
0.03
ND
16621
8/28/99
vbip
vdib
ppby
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
VOID
16802
9/9/99
IP/i/99
O9I$033
ppbv
1.41
0.47
ND
1.18
0.06
ND
0.06
0.05
0.01
0.02
0.02
0.04
ND
16891
9/21/99
10/13/§9
O9JM013
ppbv
0.60
0.29
ND
0.47
0.04
0.004
0.05
0.02
ND
0.02
0.02
0.02
ND
u - Concentration is below the detection limit
-------
FIELD BLANK DATA
Sample site: Underbill, VT
RAW AMOUNT
Derivatized Cone. (ug/mL)
Data File ID
FBID
Sample date
Date Analyzed
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyr/lsobutyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyd<
Q8J#010
14817 FB
9/14/98
10/29/98
O9CS012
15546FB
3/13/99
3/30/99
O9HQ009
16267FB
7/17/99
8/18/99
0.08
0.21
0.00
0.37
0.00
0.00
0.50
0.03
0.00
0.00
0.00
0.00
0.00
0.06
0.09
0.00
0.18
0.00
0.00
' 0.00
0.00
0.00
0.00
0.03
0.01
0.00
0.10
0.08
0.00
0.12
0.01
0.01
0.10
0.03
0.00
0.02
0.00
0.02
0.00
Field Blanks
Underivatized Conc.(total ug)
Data File ID
FBID
Date Analyzed
Q8J#010
1481 7 FB
10/29/98
O9C$012
15546FB
3/30/99 .
O9HQ009
16267FB
8/18/99
Formaldehyde
Acetaldehyde
Acrolein
Acetone
Propionaldehyde
Crotonaldehyde
Butyraldehyde
Benzaldehyde
Isovaleraldehyde
Valeraldehyde
Tolualdehydes
Hexaldehyde
2,5-Dimethylbenzaldehyde
0.04
0.16
ND
0.36
ND
ND
0.57
0.05
ND
ND
ND
ND
ND
0.03
0.07
ND
0.17
ND
ND
ND
ND
ND
ND
0.04
0.01
ND
0.07
0.08
ND
0.14
0.01
0.01
0.15
0.05
ND
0.03
ND
0.04
ND
7 of 7
-------
United States Office of Air Quality Planning and Standards Publication No. EPA-454/R-03-001
Environmental Protection Emissions, Monitoring and Analysis Division May 2000
Agency Research Triangle Park, NC
-------