Prepared for: U.S. Environmental Protection Agency (EPA), Clean Air Markets Division
EPA Contract No.: 68HERH21D0006, CASTNET Base Program (1003)

Prepared by: WSP USA Environment & Infrastructure Inc. (WSP), Gainesville, Florida
WSP Project No.: 6064226103
Submitted: March 31, 2023

Introduction

This quarterly report summarizes the Clean Air Status and Trends Network (CASTNET) data
collected during fourth quarter 2022. Trends in pollutants measured at eastern and western
reference sites are shown. Results from the quality assurance/quality control (QA/QC) program are
presented for fourth quarter data and include completeness and precision of filter concentrations
and hourly 03 concentrations. This report also analyzes data for continuous, trace-level NOy from
the six of eight sites that were operational during fourth quarter and continuous S02 concentrations
from three sites. Other QC statistics are given in the CASTNET Fourth Quarter 2022 Quality
Assurance Report with 2022 Annual Summary (Wood, 2023).

Figure 1. Fourth Highest Daily Maximum 8-hour Average 03 Concentrations (ppb) through Fourth
Quarter 2022

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EPA Contract No. 68HERH21D0006

CASTNET Quarterly Data Summary - Fourth Quarter 2022

Figure 1 shows fourth highest daily maximum 8-hour average (DM8A) 03 concentrations measured
through fourth quarter 2022. Four western sites and one eastern site exceeded the 0.070 parts per
million (ppm) National Ambient Air Quality Standard for 03_. The concentration of 83 ppb measured
at CAV436 in southeastern New Mexico was produced by emissions from oil and gas exploration,
drilling, processing, and storage in the Permian Basin. Vehicular emissions from truck traffic on
U.S. Route 285 also contributed (Sive, 2023).

Trends

Trend analyses were performed based on filter pack pollutant concentrations measured in
micrograms per cubic meter (|jg/m3) of air at the 34 eastern and 16 western reference sites during
fourth quarter. Trends in quarterly mean filter pack and 03 concentrations are shown using box
plots in Figures 2 through 13.

Fourth Quarter Concentrations

Quarterly mean S024, HN03, and K+ concentrations decreased at eastern sites in 2022, and NO~3,
NH4, total NO"3, S02, CI", Ca2+, Mg2+, and Na+ concentrations increased. Quarterly mean HN03, total
NO"3, CI", Ca2+, K+, Mg2+, and Na+ concentrations decreased at western sites in 2022 while S02,
SO4", N03, and NH4, increased.

Quarterly 03 concentrations were analyzed using box plots constructed by averaging all valid
hourly 03 concentrations within fourth quarter 2022 by site and then averaging those averages for
all eastern and western reference sites (Figure 13). The figure shows a slight overall increase in
quarterly mean 03 concentrations at eastern sites. Mean 03 concentrations at western sites
decreased in fourth quarter 2022. Quarterly mean concentrations were higher at the western
reference sites than at the eastern sites.

Figure 2. Trends in Fourth Quarter Mean HN03 Concentrations

Western Reference Sites	Eastern Reference Sites

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CASTNET Quarterly Data Summary- Fourth Quarter 2022

Figure 3. Trends in Fourth Quarter Mean N03 Concentrations
Western Reference Sites

Eastern Reference Sites

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Figure 4. Trends in Fourth Quarter Mean l\ll-f4 Concentrations
Western Reference Sites

Eastern Reference Sites



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Figure 5. Trends in Fourth Quarter Mean Total N03 Concentrations

Western Reference Sites

Eastern Reference Sites

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CASTNET Quarterly Data Summary- Fourth Quarter 2022

Figure 6. Trends in Fourth Quarter Mean S02 Concentrations
Western Reference Sites

Eastern Reference Sites

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Figure 7. Trends in Fourth Quarter Mean SO - Concentrations
Western Reference Sites

Eastern Reference Sites

10
08
0.6
0.4

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Figure 8. Trends in Fourth Quarter Mean CI" Concentrations
Western Reference Sites

Eastern Reference Sites

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CASTNET Quarterly Data Summary- Fourth Quarter 2022

Figure 9. Trends in Fourth Quarter Mean Ca Concentrations
Western Reference Sites

Eastern Reference Sites

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Figure 10. Trends in Fourth Quarter Mean K° Concentrations
Western Reference Sites

Eastern Reference Sites

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CASTNET Quarterly Data Summary- Fourth Quarter 2022

Figure 12. Trends in Fourth Quarter Mean Na' Concentrations
Western Reference Sites

Eastern Reference Sites

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Figure 13. Trends in Fourth Quarter Mean 03 Concentrations
Western Reference Sites

Eastern Reference Sites

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Changes in 3-year Average Fourth Quarter Concentrations

As shown in Table 1 and Table 2, three-year averages of quarterly mean concentrations of total
NO,, NH4, S02, and S024" were reduced over the period 1990-1992 through 2020-2022 for eastern
reference sites and from 1996-1998 through 2020-2022 for western reference sites. Potassium
levels declined at eastern sites from 2004-2006 through 2020-2022 while Ca \ Mg2+, Na', and CI"
values increased. At western sites, Na+ levels decreased while CI" and base cation concentrations
increased. Ozone concentrations increased at eastern sites and showed no change at western
reference sites.

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CASTNET Quarterly Data Summary - Fourth Quarter 2022

Table 1. Eastern Reference Sites: 3-Year Mean Values (ppb or jjg/m3)

Parameter

o3

(PPb)

Total

no3

nh;

so2

so*

Ca2+

K+

¦ a 2+

Mg

Na+

CI"

1990-1992

24

2.9

1.4

10.6

3.6











2004-2006











0.23

0.07

0.04

0.10

0.07

2020-2022

25

1.3

0.4

0.5

0.8

0.27

0.06

0.04

0.10

0.09

Percent
Change

7

-55

-72

-96

-78

14

-3

11

3

39

Note: Ozone concentrations are given as ppb. Concentrations for all other parameters are in |jg/m3.

Table 2. Western Reference Sites: 3-Year Mean Values (ppb or jjg/m3)

Parameter

o3

(PPb)

Total

no3

nh;

so2

so*

Ca2+

K+

• a 2+

Mg

Na+

CI"

1990-1992

38

0.8

0.2

0.7

0.6











2004-2006











0.10

0.03

0.02

0.06

0.03

2020-2022

38

0.5

0.1

0.2

0.3

0.18

0.03

0.02

0.06

0.04

Percent
Change

0

-39

-41

-70

-45

81

28

30

-9

22

Note: Ozone concentrations are given as ppb. Concentrations for all other parameters are in |jg/m3.

Time Series of Laboratory Analysis Parameters for All Sites

Figures 14 through 23 give time series of laboratory-analyzed concentrations of field samples and
field blanks in milligrams per liter (mg/L) of 11 parameters from first quarter 2020 through fourth
quarter 2022. These figures provide indications of potential issues with concentration
measurements relative to detection and reporting limits.

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CASTNET Quarterly Data Summary- Fourth Quarter 2022

Figure 14. Concentrations of N03 (as N) from Nylon Filters

Note: Nominal reporting limit is 0.008 mg/L.

Figure 15. Concentrations of N03 (as N) from Teflon Filters

<§'&•$'•? •&<£'	<§*<§* \^
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EPA Contract No. 68HERH21D0006

CASTNET Quarterly Data Summary- Fourth Quarter 2022

Figure 16. Concentrations of Nhf4 (as N) from Teflon Filters

• All Samples • Median • Field Blanks

Note: Nominal reporting limit is 0.020 mg/L.

Figure 17. Concentrations of S02 from K2C03-impregnated Cellulose Filters

• All Samples • Median * Field Blanks

Note: Nominal reporting limit is 0.040 mg/L.

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CASTNET Quarterly Data Summary- Fourth Quarter 2022

Figure 18. Concentrations of SOt from Nylon Filters

• All Samples • Median * Field Blanks

0.5-

0.4-

O)

E

c
o

0.3-

c 0 2-

s vf ' Cs' o' v  Q> <3°Cr Q> Qr <5° V5 V N^Qj CT
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EPA Contract No. 68HERH21D0006

CASTNET Quarterly Data Summary- Fourth Quarter 2022

Figure 20. Concentrations of CI" from Teflon Filters



Note: Nominal reporting limit is 0.020 mg/L.

0\^CS3CN^CV,oPc\v oP CV> to3 O n. ^C\ C\^CN3C>rCV,C>P
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EPA Contract No. 68HERH21D0006

CASTNET Quarterly Data Summary- Fourth Quarter 2022

Figure 22. Concentrations of K+ from Teflon Filters

0.20-

J 0.15"

O)

E,

c
o

03 °-10"

fa
C
<1)
o
c

o 0.05-

o.oo-



Note: Nominal reporting limit is 0.006 mg/L.

Figure 23. Concentrations of Mg from Teflon Filters

® All Samples ~ Median Field Blanks

• All Samples • Median * Field Blanks

Note: Nominal reporting limit is 0.003 mg/L.

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CASTNET Quarterly Data Summary- Fourth Quarter 2022

Figure 24. Concentrations of Na+ from Teflon Filters

Note: Nominal reporting limit is 0.005 mg/L.

Time Series of Concentration Differences from Co-located Sites

Figures 25 and 26 show times series of concentration differences between the two sets of co-
located sites.

Figure 25. Time Series of Filter Concentration Differences between MCK131 and MCK231, KY

0.3

0.2

Teflon SO
"eflon Ca2
Nylon SO2,

Teflon NO,
""eflon Mg'~
Nylon HNO

Teflon NHI
-•-Teflon Na+
-•-Cellulose S02

Teflon CI"
Teflon K+

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CASTNET Quarterly Data Summary - Fourth Quarter 2022

Figure 26. Time Series of Filter Concentration Differences between ROM406 and ROM206, CO

0.3

0)

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£Z

CO

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0.2

UJ



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CO

CM
CM

iB

CM

c3 
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EPA Contract No. 68HERH21D0006

CASTNET Quarterly Data Summary - Fourth Quarter 2022

Precision of Filter Pack Concentrations

Table 3 shows mean absolute relative percent differences (MARPD) for concentrations measured
at MCK131/231 and ROM406/206 during fourth quarter 2022. The MARPD values met the
20 percent criterion.

Table 3. Precision (MARPD) for Co-located Filter Pack Data during Fourth Quarter 2022



Total

no3

hno3

no3

NH+4

so2

SO4

Ca2+

n 
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EPA Contract No. 68HERH21D0006

CASTNET Quarterly Data Summary - Fourth Quarter 2022

Completeness for Filter Pack Concentrations

Table 4 shows CASTNET sites with less than 90 percent completeness for weekly filter pack concentrations. Comments are included to
provide information on why these sites experienced low data completeness.

Table 4. Sites with less than 90 Percent Data Completeness for Filter Concentrations for Fourth Quarter 2022 (1 of 2)

Site ID

Teflon

so*

Teflon

no3

Teflon

nh;

Teflon
Minor
Cations

Teflon

cr

Nylon

hno3

Nylon

so*

Cellulose

so2

Comment

ALH157, IL

69.2

69.2

69.2

69.2

69.2

69.2

69.2

69.2

Site was decommissioned 12/6/22.

ANA115, Ml

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

Site was moth balled due to EPA's
FY2022 budget.

ASH135, ME

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

Site was moth balled due to EPA's
FY2022 budget.

BWR139, MD

76.9

76.9

76.9

76.9

76.9

76.9

76.9

76.9

There were two 2-week samples during
the quarter. Another sample was
invalidated because of a hole in the
Teflon filter.

CDR119, WV

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

Site was moth balled due to EPA's
FY2022 budget.

CDZ171, KY

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

Site was moth balled due to EPA's
FY2022 budget.

DCP114, OH

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

Site was moth balled due to EPA's
FY2022 budget.

EGB181, ON

61.5

61.5

61.5

61.5

61.5

61.5

61.5

61.5

Communication issues occurred. Data
were missing from 11/6/22 to 12/5/22.

HWF187, NY

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

Site was moth balled due to EPA's
FY2022 budget.

LAV410, CA

84.6

84.6

84.6

84.6

84.6

84.6

84.6

84.6

A power failure affected two samples.

MKG113, PA

53.8

53.8

53.8

53.8

53.8

53.8

53.8

53.8

The mass flow controller malfunctioned in
mid-October, and its replacement
malfunctioned in late November. Six
samples were affected.

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CASTNET Quarterly Data Summary - Fourth Quarter 2022

Table 4. Sites with less than 90 Percent Data Completeness for Filter Concentrations for Fourth Quarter 2022 (2 of 2)

Site ID

Teflon

so*

Teflon

no3

Teflon

nh;

Teflon
Minor
Cations

Teflon
CI"

Nylon

hno3

Nylon

so*

Cellulose

so2

Comment

PED108, VA

84.6

84.6

84.6

84.6

84.6

84.6

84.6

84.6

One sample was invalidated for
insufficient flow volume. Another was
affected by power outage.

PNF126, NC

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

Site was moth balled due to EPA's
FY2022 budget.

PSU106, PA

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

Site was moth balled due to EPA's
FY2022 budget.

UND002, VT

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

Site was moth balled due to EPA's
FY2022 budget.

UVL124, Ml

69.2

69.2

69.2

69.2

69.2

69.2

69.2

69.2

The mass flow controller malfunctioned in
early October and was replaced on
11/1/2022. Four samples were
invalidated.

VOY413, MN

84.6

84.6

84.6

84.6

84.6

84.6

84.6

84.6

A flow system leak affected two samples.

VPI120, VA

84.6

84.6

84.6

84.6

84.6

84.6

84.6

84.6

There was one 2-week sample. Another
was invalidated due to power failure.

WST109, NH

0.0

0.0

0.0

0.0

0.0

0.0

0.0

0.0

Site was moth balled due to EPA's
FY2022 budget.

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CASTNET Quarterly Data Summary - Fourth Quarter 2022

Precision of Ozone Concentrations

Time series of co-located hourly 03 concentration differences for fourth quarter 2022 are provided
in Figures 27 and 28 for MCK131/231 and ROM406/206, respectively. The figures indicate no
consistent bias between the co-located analyzers at these site locations.

Figure 27. Time Series of the Differences in Co-located 03 Concentrations for MCK131/231, KY
4 	

-4

OJ

OJ

OJ

OJ

OJ

OJ

CM

OJ

OJ

OJ

I

OJ

OJ

OJ

OJ

OJ

OJ

OJ

OJ

OJ

T—

T—

T—

T—

o

o

o

o

o

o

o

T—

OJ

CO

T—

OJ

CO

T—

OJ

CO



o

o

o



T—



OJ

OJ

OJ



T—

T—

T—

T—

T—

T—

T—

T—

T—

Figure 28. Time Series of the Differences in Co-located 03 Concentrations for ROM406/206, CO
6

CM
CM

CM
CM

CM
CM

CM
o

CM
OJ

CO
O

CM
OJ
O

OJ
OJ
O
OJ

OJ
OJ
O

CO

OJ
OJ

o

OJ

OJ
OJ

o

OJ
OJ

OJ
OJ

o

CO
OJ

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CASTNET Quarterly Data Summary - Fourth Quarter 2022

Table 5 gives MARPD data for 03 data measured at the two co-located sites.

Table 5. Quarterly Precision (MARPD) for Co-located 03 Concentrations

Site Pair

Quarter

Start Date

MARPD

Records

MCK131/231, KY



4

1/1/22

1.1

2046



1

4/1/22

0.6

2066



2

7/1/22

0.8

2058



3

10/1/22

0.6

2098

ROM406/206, CO



4

1/1/22

2.0

1970



1

4/1/22

1.5

1932



2

7/1/22

1.8

1638



3

10/1/22

1.5

1531

Completeness for 03 Concentrations

Calculation of an annual 03 value requires 75 percent completeness. However, calculation of the
3-year design value used for regulatory purposes requires 90 percent completeness. Table 6
shows CASTNET sites with less than 90 percent completeness for DM8A 03 concentrations.
Comments are provided for these sites.

Table 6. Sites with less than 90 Percent Data Completeness for DM8A Concentrations during
Fourth Quarter 2022

Site ID

Percent
Completeness

Comments

ASH135, ME

0

Site was mothballed due to EPA's FY2022 budget.

HWF187, NY

0

Site was mothballed due to EPA's FY2022 budget.

WST109, NH

0

Site was mothballed due to EPA's FY2022 budget.

PNF126, NC

0

Site was mothballed due to EPA's FY2022 budget.

CDZ171, KY

0

Site was mothballed due to EPA's FY2022 budget.

DCP114, OH

0

Site was mothballed due to EPA's FY2022 budget.

CDR119, WV

0

Site was mothballed due to EPA's FY2022 budget.

DEN417, AK

71

Ozone data were invalid from 10/20/22 through 11/14/22 due to a
failed pump and an issue with the solenoid.

ALH157, IL

72

Site was decommissioned 12/6/22.

ROM206, CO

74

QC failures resulted from malfunctioning analyzer solenoid.
Associated data were invalidated. Analyzer was replaced 12/16/22.

ALC188, TX

74

Several sampling system issues had to be addressed following
maintenance and replacement of the analyzer in late October.
Associated data were invalidated.

LAV410, CA

82

Ozone data were invalid intermittently throughout December due to
poor QC checks and noise in the minute data trace.

NPT006, ID

88

QC failures resulted from sampling system issues in late October.
Associated data were invalidated.

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Table 7 shows CASTNET sites with less than 90 percent completeness for hourly 03
concentrations. Comments are provided for these sites. The annual average for each of these sites
is included for reference.

Table 7. Sites with less than 90 Percent Data Completeness for 03 Concentrations

Site ID

Q4 2022

Q1 2022-
Q4 2022

Comments

ALC188, TX

75

90

Several sampling system issues had to be addressed following
maintenance and replacement of the analyzer in late October.
Associated data were invalidated.

ASH135, ME

0

56

Site was mothballed due to EPA's FY2022 budget.

CDR119, WV

0

56

Site was mothballed due to EPA's FY2022 budget.

CDZ171, KY

0

60

Site was mothballed due to EPA's FY2022 budget.

DCP114, OH

0

60

Site was mothballed due to EPA's FY2022 budget.

DEN417, AK

71

89

Ozone data were invalid from 10/20/22 through 11/14/22 due
to a failed pump and an issue with the solenoid.

HWF187, NY

0

59

Site was mothballed due to EPA's FY2022 budget.

LAV410, CA

86

94

Ozone data were invalid intermittently throughout December
due to poor QC checks and noise in the minute data trace.

PNF126, NC

0

60

Site was mothballed due to EPA's FY2022 budget.

ROM206, CO

74

92

QC failures resulted from a malfunctioning analyzer solenoid.
Associated data were invalidated. Analyzer was replaced
12/16/22.

WST109, NH

0

60

Site was mothballed due to EPA's FY2022 budget.

Filter Pack Total Nitrate and Continuous Trace-level NOy Concentrations at CASTNET Sites

Figures 29 through 36 show a comparison of weekly average continuous NOy measurements with
weekly filter pack total NOj concentrations collected at the six of eight sites with NOy
measurements. The NOy concentrations were consistently higher than the total NO"3 levels at all
sites. The average weekly NOy levels, the weekly total NO"3 concentrations, and their ratios for the
six sites with available data are shown in Table 8. Ratios of NOy to total NO"3 varied from 4.82 at
MAC426 to 8.22 at PND165. No data are available from HWF187 and PNF126 for fourth quarter
2022. These sites were mothballed due to EPA's budget constraints.

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Table 8. Summary of Total N03 and N0y Measurements for Fourth Quarter 2022

Site ID

Elevation

Total NO~3 (ppb)

NOy (ppb)

Ratio

DUK008, NC

164*

0.71

2.89

5.87

BVL130, IL

213

0.98

4.57

5.44

MAC426, KY

243

0.57

2.55

4.82

HWF187, NY*

497

-

-

-

GRS420, TN

793

0.35

1.76

5.47

PNF126, NC *

1216

-

-

-

PND165, WY

2386

0.08

0.67

8.22

ROM206, CO

2742

0.12

0.82

7.37

Note: The inlet of the enhanced NOy monitor is located at the top of the 30-meter tower.

* The site was mothballed in second quarter 2022 due to EPA's FY2022 budget. No measurements were recorded
during fourth quarter 2022.

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Figure 30. Comparison of BVL130 Weekly Mean NOy and Total NO"3 Concentrations

	T 5

-¦-Mean Continuous NOy
-~-Filter Pack Total Nitrate

Figure 31. Comparison of MAC426 Weekly Mean NOy and Total NO"3 Concentrations

-¦-Mean Continuous NOy
-~—Filter Pack Total Nitrate

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32. Comparison of HWF187 Weekly Mean NOy and Total NO"3 Concentrations

O.i

-Mean Continuous NOy
-Filter Pack Total Nitrate

0.6

0.4

Site mothballed due to EPA's FY2022 budget.

TO

0

0.2 o
c
o
O
o
ro

0.0 £

-0.2

-0.4

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Figure 34. Comparison of PNF126 Weekly Mean NOy and Total NO"3 Concentrations

1.5

-Mean Continuous NOy
-Filter Pack Total Nitrate

1.0

Site mothballed due to EPA's FY2022 budget.

0.5

0.0

1.2

1.0

O.i

0.6

0.4

0.2

0.0

Figure 35. Comparison of PND165 Weekly Mean NOy and Total NO"3 Concentrations

-•-Mean Continuous NOy
-~-Filter Pack Total Nitrate

0.05 J

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Figure 36. Comparison of ROM206 Weekly Mean NOy and Total NO"3 Concentrations

-¦-Mean Continuous NOy
-~—Filter Pack Total Nitrate

Filter Pack and Continuous Trace-level Gas Sulfur Dioxide Concentrations

Figures 37 through 39 provide diagrams that compare weekly filter pack S02 concentrations with
continuous trace-level gas data measured at BVL130, MAC426, and GRS420. The continuously
measured trace-level concentrations were higher than filter pack concentrations during the first four
weeks of fourth quarter at BVL130 and then were comparable. The filter pack concentrations were
higher than continuous concentrations at MAC426. The S02 data completeness was insufficient
at GRS420.

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Figure 37. Comparison of BVL130 Weekly Mean S02 Concentrations

Figure 38. Comparison of MAC426 Weekly Mean S02 Concentrations

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Figure 39. Comparison of GRS420 Weekly Mean S02 Concentrations

0.4

—¦— Mean Continuous S02
—Filter Pack S02

0.0

Completeness for Continuous Trace-level Gas Measurements

Table 9 shows the percent completeness for CASTNET trace-level gas measurements. Comments
are provided for sites with less than 90 percent completeness for hourly trace-level gas
concentrations during fourth quarter 2022. The average for first quarter 2022 through fourth quarter
2022 for each of the sites is included for reference.

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Table 9 Percent Data Completeness for Continuous Trace-level Gas Measurements (1 of 2)

Site ID

Parameter*

Q4 2022

Q1 2022 -
Q4 2022

Comments

BVL130, IL

CO

18

43

The CO system was subject to intermittent
analyzer stability issues throughout the
quarter.

NO

59

79

QC failures occurred in December. Associated
data were invalidated.

NOY

33

77

The converter and ozone generator
malfunctioned beginning in late October. Both
were replaced by early December. Associated
data were invalidated.

NOYDIF

33

73

S02_GA

86

88

Data were invalid during several multipoint
calibrations.

CHC432, NM

NO

98

98



NOX

98

98

NOXDIF

98

98

DUK008, NC

HN03

43

75

Data were invalidated 11/23/23 to 12/14/23 for
high noise levels and 12/23/23 to 12/26/23 for
high shelter temperatures. An additional week
of data was not collected due to a power
failure. HN03 and NOY Minus were invalidated
10/25/23 and 11/8/23 for suspect values.

NH3

57

61

NO

57

79

N02 TRUE

57

79

NOX TRUE

57

79

NOY

57

79

NOY MINUS

43

75

NOYDIF

57

79

TNX

57

64

GRS420, TN

CO

93

83



NO

94

88

NOY

94

88

NOYDIF

94

87

S02_GA

62

78

The lamp was failing. Associated data were
invalidated.

HWF187, NY

NO

0

33

Site mothballed due to EPA's FY2022 budget.

NOY

0

32

NOYDIF

0

32

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Table 9 Percent Data Completeness for Continuous Trace-level Gas Measurements (2 of 2)

Site ID

Parameter*

Q4 2022

Q1 2022 -
Q4 2022

Comments

MAC426, KY

CO

91

94



NO

96

97

NOY

96

97

NOYDIF

96

97

S02_GA

78

92

S02 data invalid from 11/26/22 through
12/13/22 because the instrument changed its
background and intercept frequently
throughout this period.

PND165, WY

NO

93

85

Site mothballed due to EPA's FY2022 budget.

NOY

91

83

NOYDIF

91

83

PNF126, NC

NO

0

33

Site mothballed due to EPA's FY2022 budget.

NOY

0

33

NOYDIF

0

33

ROM206, CO

NO

95

95



NOY

95

95

NOYDIF

95

95

Note: * See Table 10

The parameters listed in Table 9 are both calculated and measured. Table 10 provides information
on how the parameters listed in Table 9 are obtained.

Table 10. CASTNET Trace-level Gas Measurements

Parameter Name

How Obtained

Description of Process

CO

Measured

Gas filter correlation

HN03

Calculated

NOY minus NOY_MINUS

NH3

Calculated

TNX minus NOY

NO

Measured

Chemiluminescence reaction/no converter used

N02_TRUE

Calculated

NOX_TRUE minus NO

NOX_TRUE

Measured

Photolytic converter

NOY

Measured

Molybdenum converter at 315° Celsius

NOYDIF

Calculated

NOY minus NO

NOY_MINUS

Measured

Sodium carbonate denuder followed by molybdenum converter at
315° Celsius

NOX

Measured

Molybdenum converter at 325° Celsius

NOXDIF

Calculated

NOX minus NO

S02_GA

Measured

Ultraviolet fluorescence

TNX

Measured

Platinum/stainless steel converter at 825° Celsius followed by
molybdenum converter at 315° Celsius

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References

Sive, Barkley C., Prenni, Anthony J., Gebhart, Kristi A., Schichtel, Bret A., Stacy, Andrea, Vimont,
John, Benedict, Katherine B., Zhou, Yong, Pan, Da, Marsavin, Andrey, Naimie. Lillian,
Pollack, Nana, Fischer, Emily V., Sullivan, Amy P., Collet, Jeffrey L. Jr., George, Ingrid,
Sather, Mark Sather, Apodaca, Suzanne, Luke, Winston, Mao, Huiting. 2023. Volatile
Organic Compound and Ozone Measurements at Carlsbad Caverns National Park: Impacts
of Oil and Natural Gas Operation Emissions on Park Air Quality. Presented at the American
Meteorological Society Annual Meeting, January 8-12, Denver.

Wood Environment & Infrastructure Solutions, Inc. 2022. Clean Air Status and Trends Network
(CASTNET) Fourth Quarter 2022 Quality Assurance Report.
https://java.epa.gov/castnet/documents.do

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