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Effects of Wind Direction on VOC
Concentrations in Southeast Kansas
Sergio A. Guerra, Dennis D. Lane, Glen A. Marotz,
Ray E. Carter, Carrie M. Hohl, Richard W. Baldauf
Department of Civil, Environmental, and Architectural
Engineering, University of Kansas
Introduction


Southeast Kansas supports the highest concentration of
hazardous waste burners in the country





U.S. EPA sponsored the Southeast Kansas Health Study
to investigate air quality and potential health effects
from ambient air in the area




3 cement kilns
1 commercial hazardous waste incinerator

(report available at http://www2.kumc.edu/ceoh/skhs/)

This study was a joint effort between the Department of
Civil and Environmental Engineering at KU and the KU
Medical Center
Scope






The environmental sampling element of
the project included the collection of 24-hr
VOC samples at selected sites in
Southeast Kansas
Effects of spatial and temporal factors on
these concentrations were investigated
Wind direction effects are of particular
interest
Air Quality Monitoring








Duration of Monitoring - March, 1999
through October, 2000
Sampling Sites in the cities of Chanute,
Coffeyville, Fredonia, and Independence
Additional Sites in Sedan, Tyro, Labette
County
Sampling Site Design, Sampling and
Analysis Protocols According to EPA
Guidelines
Sampling Area in Southeast Kansas
Sampling Area in Southeast Kansas

Coffeyville

Chanute

Fredonia

Independence

Background

CC Ag..
House

North Ash
Grove

East
Kennel

East of
River

Labette Co.Big Hill Lake

KDHE
Site

South Ash
Grove

Lincoln
School

Eisenhower
School

Labette Co.Junction160/169

Longfellow
School

Elderly
care

South
Farm

Radio
Tower

Sedan- Power
Pole

Admin.
Building

KDHE
office

South
Mound

Washington
School

Tyro- Water
Tower

Airport
Source-specific sites


Wichita windrose
(1984-1992)
Fredonia

Site

Sampling Methods

LaF-2

PM10 MiniVol*

LaF-3**

PM10 MiniVol

LaF-5

PM2.5 MiniVol
PM10 MiniVol

**Site was discontinued after March, 2000.
Data Collection- Canister with flow
controller and programmable
open/close valve
Sample analysis by GC/MS


VOCs analyzed
included:








Benzene
Toluene
Xylene isomers
Trichloroethene
Tetracholoethene
Chloroform
1,1,1trichloroethene
Data Analysis




Descriptive statistics were calculated for
the VOC concentrations
Data was analyzed for



Possible effects of sampling site
Possible effects of sampling date
Data Analysis


The temporal factor was further investigated to
determine the effect of wind direction on VOC
concentrations


Data was divided in four wind direction categories (from NCDC);







South
North
Calm/variable
Other

The effect of the targeted sources was also analyzed by
using the Wilcoxon signed rank test for the cities of
Chanute, Independence and Fredonia
Ambient Air VOC Concentrations
Producing Increased Cancer Risks
Increased Cancer Risks VOC

Concentration (µg/m3) producing risk levels
1 in 10,000

1 in 100,000

1 in 1,000,000

benzene

13

1.3

0.13

Bromoform*

90

9

0.9

carbon tetrachloride

7

0.7

0.07

Chloroform

4

0.4

0.04

1,2-dibromoethanea

0.5

0.05

0.005

1,2-dichloroethanea

4

0.4

0.04

1,1-dichloroethylenea

2

0.2

0.02

Hexachlorobutadienea

5

0.5

0.05

methylene chloride

200

20

2

1,1,1,2-tetrachloroethanea

10

1

0.1

1,1,2,2-tetrachloroethanea

2

0.2

0.02

170

17

1.7

1,1,2-trichloroethanea

6

0.6

0.06

Trichloroethylene

60

6

0.6

Tetrachloroethylene

* - not detected during this study
Ambient Air VOC Concentrations
Producing Other Health Effects
Other Health Effects
VOC

Minimum concentration producing health effects (µg/m3)

benzene

60

carbon tetrachloride

40

chlorobenzene

20

chloroethanea

10,000

chloroform

300

chloromethanea

90

dichlorobenzene isomersa

800

1,1-dichloroethanea

500

ethylbenzene

1000

methylene chloride

3000

naphthalene

3

styrene

1000

tetrachloroethylene

300

toluene

400

1,1,1-trichloroethane

1000

trichloroethylene

500

xylene isomers

400
Results
Distribution of VOC Concentrations,
24-hour samples
VOC

Number of Samples with Concentration in Each Range
0.1-1.0g/L

1.1-10.0g/L

10.1-100.0g/L

>100g/L

Health Effectsa

Benzene

54

6

0

0

58

Toluene

40

113

36

6

5

Ethylbenzene

16

56

20

10

2

m,p-xylene

32

42

4

0

0

o-xylene

36

32

0

0

0

Styrene

9

16

17

2

0

Naphthalene

76

46

1

0

14

Chlorobenzene

5

4

0

0

0

methylene chloride

3

26

8

2

31

Chloroform

12

6

0

0

18

carbon tetrachloride

28

2

0

0

30

1,1,1-TCA

7

1

1

0

0

Trichloroethylene

2

12

19

12

44

Tetrachloroethylene

3

16

2

0

14

Isooctane

1

19

7

0

na
VOC observations








Although there are 58 samples with benzene concentrations
exceeding the 1-in-1,000,000 level of increased cancer risk, only 5
of those exceeded the 1-in-100,000 level; none exceeded the 1-in10,000 level.
Other non-halogenated aromatic compounds were detected in a
large number of samples, especially toluene, ethylbenzene, and
naphthalene. However, only in the case of naphthalene were there
more than ten samples with concentrations which could produce
health effects.
There were 31 samples with methylene chloride concentrations
exceeding the 1-in-1,000,000 level of increased cancer risk. Only
eight of those exceeded the 1-in-100,000 level, and only one
exceeded the 1-in-10,000 level.
There were 18 samples with chloroform concentrations exceeding
the 1-in-1,000,000 level of increased cancer risk, thirteen of which
exceeded the 1-in-100,000 level, and two of which exceeded the 1in-10,000 level.
VOC observations






There were 30 samples with carbon tetrachloride
concentrations exceeding the 1-in-1,000,000 level of
increased cancer risk, fourteen of which exceeded the 1in-100,000 level; none exceeded the 1-in-10,000 level of
increased risk.
There were 44 samples with trichloroethylene
concentrations exceeding the 1-in-1,000,000 level of
increased cancer risk. Of those, 38 exceeded the 1-in100,000 level and 21 exceeded the 1-in-10,000 level.
There were fourteen samples with tetrachloroethylene
concentrations exceeding the 1-in-1,000,000 level of
increased cancer risk, only one of which the 1-in100,000 level.
Effects of sampling site






Sampling site was a statistically significant factor for 8 of
the 15 VOCs.
Site factor was further analyzed using upwind/downwind
sample pairs.
In Chanute and Fredonia, higher concentrations of six
VOCs were found in upwind samples.






Differences were not statistically significant in Fredonia, but
were in Chanute for toluene, ethylbenzene, and xylene.
Results indicate contributions from other sources.

In Independence, significantly higher concentrations of
ethylbenzene, styrene, methylene chloride, and
trichloroethylene were found in downwind samples.


Results indicate contribution from targeted source.
Effects of sampling date




Sampling date was a significant factor for 12 of the 15
VOCs
Wind direction accounted for much of the variation
among sampling dates.




Northerly winds frequently produced higher concentrations of
benzene and xylene, and occasionally produced higher
concentrations of carbon tetrachloride.
Southerly winds frequently produced higher concentrations of
toluene, but lower concentrations of naphthalene.
Conclusions




Fifteen VOCs were detected above detection limit.
Several VOCs were found at concentrations above published risk
levels, although infrequently.
Trichloroethylene concentrations were of most concern







44 values exceeded the 1 in 1,000,000 risk level
21 of those exceeded the 1 in 10,000 risk level

Statistical analysis showed that sampling site had a significant effect
on the concentrations of many compounds.
Larger than expected highest values were also found at the
Coffeyville-KDHE and Chanute-S. Ash Grove sites.
Sampling date was found to be significant for many of the
compounds.



Wind direction was shown to be a significant factor but not consistently.
For example, southerly winds typically produced higher than expected
conc. of toluene but lower than expected conc. of naphthalene.
Conclusions








For four of the compounds, concentrations at sites
downwind from the targeted source in Independence
were significantly higher than concentrations at upwind
sites.
However, in Chanute and Fredonia concentrations were
significantly higher at upwind sites.
During the present study several VOCs were found
above concentrations that could potentially affect human
health, though these levels were infrequent.
It could not be shown conclusively that targeted sources
contributed significantly to these concentrations.

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Effects of Wind Direction on VOC Concentrations in Southeast Kansas

  • 1. Effects of Wind Direction on VOC Concentrations in Southeast Kansas Sergio A. Guerra, Dennis D. Lane, Glen A. Marotz, Ray E. Carter, Carrie M. Hohl, Richard W. Baldauf Department of Civil, Environmental, and Architectural Engineering, University of Kansas
  • 2. Introduction  Southeast Kansas supports the highest concentration of hazardous waste burners in the country    U.S. EPA sponsored the Southeast Kansas Health Study to investigate air quality and potential health effects from ambient air in the area   3 cement kilns 1 commercial hazardous waste incinerator (report available at http://www2.kumc.edu/ceoh/skhs/) This study was a joint effort between the Department of Civil and Environmental Engineering at KU and the KU Medical Center
  • 3. Scope    The environmental sampling element of the project included the collection of 24-hr VOC samples at selected sites in Southeast Kansas Effects of spatial and temporal factors on these concentrations were investigated Wind direction effects are of particular interest
  • 4. Air Quality Monitoring     Duration of Monitoring - March, 1999 through October, 2000 Sampling Sites in the cities of Chanute, Coffeyville, Fredonia, and Independence Additional Sites in Sedan, Tyro, Labette County Sampling Site Design, Sampling and Analysis Protocols According to EPA Guidelines
  • 5. Sampling Area in Southeast Kansas
  • 6. Sampling Area in Southeast Kansas Coffeyville Chanute Fredonia Independence Background CC Ag.. House North Ash Grove East Kennel East of River Labette Co.Big Hill Lake KDHE Site South Ash Grove Lincoln School Eisenhower School Labette Co.Junction160/169 Longfellow School Elderly care South Farm Radio Tower Sedan- Power Pole Admin. Building KDHE office South Mound Washington School Tyro- Water Tower Airport
  • 8. Fredonia Site Sampling Methods LaF-2 PM10 MiniVol* LaF-3** PM10 MiniVol LaF-5 PM2.5 MiniVol PM10 MiniVol **Site was discontinued after March, 2000.
  • 9. Data Collection- Canister with flow controller and programmable open/close valve
  • 10. Sample analysis by GC/MS  VOCs analyzed included:        Benzene Toluene Xylene isomers Trichloroethene Tetracholoethene Chloroform 1,1,1trichloroethene
  • 11. Data Analysis   Descriptive statistics were calculated for the VOC concentrations Data was analyzed for   Possible effects of sampling site Possible effects of sampling date
  • 12. Data Analysis  The temporal factor was further investigated to determine the effect of wind direction on VOC concentrations  Data was divided in four wind direction categories (from NCDC);      South North Calm/variable Other The effect of the targeted sources was also analyzed by using the Wilcoxon signed rank test for the cities of Chanute, Independence and Fredonia
  • 13. Ambient Air VOC Concentrations Producing Increased Cancer Risks Increased Cancer Risks VOC Concentration (µg/m3) producing risk levels 1 in 10,000 1 in 100,000 1 in 1,000,000 benzene 13 1.3 0.13 Bromoform* 90 9 0.9 carbon tetrachloride 7 0.7 0.07 Chloroform 4 0.4 0.04 1,2-dibromoethanea 0.5 0.05 0.005 1,2-dichloroethanea 4 0.4 0.04 1,1-dichloroethylenea 2 0.2 0.02 Hexachlorobutadienea 5 0.5 0.05 methylene chloride 200 20 2 1,1,1,2-tetrachloroethanea 10 1 0.1 1,1,2,2-tetrachloroethanea 2 0.2 0.02 170 17 1.7 1,1,2-trichloroethanea 6 0.6 0.06 Trichloroethylene 60 6 0.6 Tetrachloroethylene * - not detected during this study
  • 14. Ambient Air VOC Concentrations Producing Other Health Effects Other Health Effects VOC Minimum concentration producing health effects (µg/m3) benzene 60 carbon tetrachloride 40 chlorobenzene 20 chloroethanea 10,000 chloroform 300 chloromethanea 90 dichlorobenzene isomersa 800 1,1-dichloroethanea 500 ethylbenzene 1000 methylene chloride 3000 naphthalene 3 styrene 1000 tetrachloroethylene 300 toluene 400 1,1,1-trichloroethane 1000 trichloroethylene 500 xylene isomers 400
  • 16. Distribution of VOC Concentrations, 24-hour samples VOC Number of Samples with Concentration in Each Range 0.1-1.0g/L 1.1-10.0g/L 10.1-100.0g/L >100g/L Health Effectsa Benzene 54 6 0 0 58 Toluene 40 113 36 6 5 Ethylbenzene 16 56 20 10 2 m,p-xylene 32 42 4 0 0 o-xylene 36 32 0 0 0 Styrene 9 16 17 2 0 Naphthalene 76 46 1 0 14 Chlorobenzene 5 4 0 0 0 methylene chloride 3 26 8 2 31 Chloroform 12 6 0 0 18 carbon tetrachloride 28 2 0 0 30 1,1,1-TCA 7 1 1 0 0 Trichloroethylene 2 12 19 12 44 Tetrachloroethylene 3 16 2 0 14 Isooctane 1 19 7 0 na
  • 17. VOC observations     Although there are 58 samples with benzene concentrations exceeding the 1-in-1,000,000 level of increased cancer risk, only 5 of those exceeded the 1-in-100,000 level; none exceeded the 1-in10,000 level. Other non-halogenated aromatic compounds were detected in a large number of samples, especially toluene, ethylbenzene, and naphthalene. However, only in the case of naphthalene were there more than ten samples with concentrations which could produce health effects. There were 31 samples with methylene chloride concentrations exceeding the 1-in-1,000,000 level of increased cancer risk. Only eight of those exceeded the 1-in-100,000 level, and only one exceeded the 1-in-10,000 level. There were 18 samples with chloroform concentrations exceeding the 1-in-1,000,000 level of increased cancer risk, thirteen of which exceeded the 1-in-100,000 level, and two of which exceeded the 1in-10,000 level.
  • 18. VOC observations    There were 30 samples with carbon tetrachloride concentrations exceeding the 1-in-1,000,000 level of increased cancer risk, fourteen of which exceeded the 1in-100,000 level; none exceeded the 1-in-10,000 level of increased risk. There were 44 samples with trichloroethylene concentrations exceeding the 1-in-1,000,000 level of increased cancer risk. Of those, 38 exceeded the 1-in100,000 level and 21 exceeded the 1-in-10,000 level. There were fourteen samples with tetrachloroethylene concentrations exceeding the 1-in-1,000,000 level of increased cancer risk, only one of which the 1-in100,000 level.
  • 19. Effects of sampling site    Sampling site was a statistically significant factor for 8 of the 15 VOCs. Site factor was further analyzed using upwind/downwind sample pairs. In Chanute and Fredonia, higher concentrations of six VOCs were found in upwind samples.    Differences were not statistically significant in Fredonia, but were in Chanute for toluene, ethylbenzene, and xylene. Results indicate contributions from other sources. In Independence, significantly higher concentrations of ethylbenzene, styrene, methylene chloride, and trichloroethylene were found in downwind samples.  Results indicate contribution from targeted source.
  • 20. Effects of sampling date   Sampling date was a significant factor for 12 of the 15 VOCs Wind direction accounted for much of the variation among sampling dates.   Northerly winds frequently produced higher concentrations of benzene and xylene, and occasionally produced higher concentrations of carbon tetrachloride. Southerly winds frequently produced higher concentrations of toluene, but lower concentrations of naphthalene.
  • 21. Conclusions    Fifteen VOCs were detected above detection limit. Several VOCs were found at concentrations above published risk levels, although infrequently. Trichloroethylene concentrations were of most concern      44 values exceeded the 1 in 1,000,000 risk level 21 of those exceeded the 1 in 10,000 risk level Statistical analysis showed that sampling site had a significant effect on the concentrations of many compounds. Larger than expected highest values were also found at the Coffeyville-KDHE and Chanute-S. Ash Grove sites. Sampling date was found to be significant for many of the compounds.   Wind direction was shown to be a significant factor but not consistently. For example, southerly winds typically produced higher than expected conc. of toluene but lower than expected conc. of naphthalene.
  • 22. Conclusions     For four of the compounds, concentrations at sites downwind from the targeted source in Independence were significantly higher than concentrations at upwind sites. However, in Chanute and Fredonia concentrations were significantly higher at upwind sites. During the present study several VOCs were found above concentrations that could potentially affect human health, though these levels were infrequent. It could not be shown conclusively that targeted sources contributed significantly to these concentrations.