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Blood and exhaled air can be used for
biomonitoring of hydrofluorocarbons in
humans
Lena Ernstgård
Work environment toxicology, Institute of Environmental Medicine
Karolinska Institutet, Sweden
Introduction
Various hydrofluorocarbons (HFCs) have replaced the ozone-depleting
chlorofluorocarbons and hydrochlorofluorocarbons in refrigeration and
air-conditioning applications.
Colorless gases with faint, ethereal smell and are low-or non-flammable
at atmospheric pressure and room temperature.
Four studied HFCs; 1,1-Difluoroethane (HFC152a), 1,1,1trifluoroethane (HFC143a), 1,1,1,2-tetrafluoroethane (HFC134a), and
1,1,1,3,3-pentafluoropropane (HFC245fa).
Aim
The main objective of this study was to investigate the
possibility to use blood and exhaled air for exposure
biomonitoring of HFCs.

Exposure to HFCs, e.g. during installation or repair of refrigeration
or air-condition systems, occur as short peaks and probably locally
distributed. Air monitoring in the breathing zone, may be
misleading. In such cases, biological exposure monitoring may be
advantageous as it more closely reflects the internal exposure.
Method

Exposures for 2 h at 50 W exercise.
HFC152a (0, 500, and 1000 ppm)
HFC143a (500 ppm)
HFC134a (500 ppm)
HFC245fa (0, 100, and 300 ppm)
Sample collection 0-22 h postexposure:
Capillary blood
Exhaled air
Urine
Temperature 18°C and humidity 30%
4
Methods
Analysis of HFC in capillary blood, urine and exhaled air.
By gas-chromatography

The observed time courses in blood and exhaled air were described
with a physiologically-based pharmacokinetic (PBPK) model.
One model for all four HFC

In additional PBPK simulations, the experimental 2-h exposures were
extended to 8-h exposures to better capture occupational conditions.

5
Partition coefficients
Blood/air, and tissue/blood coefficients are essential to characterize the
uptake and disposition of volatile substances.
Experimental data on human blood:air, olive oil:air and water:air
partition coefficients of all four HFCs and HFC125a (1,1,1,2,2pentafluoroethane).

Ernstgård L, Lind B, Andersen ME, Johanson G. Liquid-air partition coefficients of 1,1-difluoroethane
(HFC152a), 1,1,1-trifluoroethane (HFC143a), 1,1,1,2-tetrafluoroethane (HFC134a), 1,1,1,2,2pentafluoroethane (HFC125) and 1,1,1,3,3-pentafluoropropane (HFC245fa). J Appl Toxicol. 2010
Jan;30(1):59-62.

6
PBPK model
The PBPK parameters (compartmental
volumes and blood flows and cardiac output)
were calculated for each individual by
allometric scaling based on body weight and
height.
Individually measured pulmonary ventilation
rates, and chamber air concentrations.
The parameters were also scaled to a 50-W
workload or to rest.
Sensitivity analyses showed that the blood:air
partition coefficient is the most sensitive
parameter.
Results
µM

Blood.

HFC152a (1000 ppm)

100

HFC143a (500 ppm)
HFC134a (500 ppm)
10

HFC245fa (300 ppm)

1
Exposure

0.1
0

60

120

180
Time (min)

240

300

360

8
Conc, µM
100

Conc, µM
100
B. 300 ppm HFC245fa

A. 1000 ppm HFC152a
10

10

1

1

0.1

0.1
0.01

0.01
0

60

120

180
Time, min

240

300

0

360

60

120

180

240

300

360

Time, min

Conc, µM

Conc, µM

100

100
D. 500 ppm HFC134a

C. 500 ppm HFC143a
10

10

1

1

0.1

0.1

0.01
0

60

120

180

240

300

360

0.01
0

Time, min
Conc, µM

60

120

180

240

300

360

Time, min

100
E. 500 ppm HFC125a
10
1
0.1
0.01
0

60

120

180

240

Time, min

300

360

9
Conc, µM

HFC152a
HFC245a
HFC134a
HFC143a
HFC125a

Blood

10

Conc, µM

Blood
10

1
1
0.1
0.1

8,0

Time, h

8,5

0.01
0

2

4

6
Time, h

8

10

12

Exhaled air
10

Exhaled air

Conc, µM

Conc, µM

10
1
1
0.1
0.1

8,0

Time, h

8,5

0.01
0

2

4

6
Time, h

8

10

12
10
HFC152a

HFC143a

HFC134a

HFC245fa

HFC125a

Concentration in blood (µM)
Immediately after exposure

11.7

2.3

4.8

7.7

1.4

30 min after exposure

3.8

0.61

1.4

2.4

0.33

0.0073

0.019

0.019

0.13

0.036

Next morning

Concentration in exhaled air (µM)
Immediately after exposure

3.8

1.1

2.1

3.0

0.65

30 min after exposure

1.2

0.28

0.59

0.87

0.16

0.0023

0.0089

0.0077

0.049

0.017

Next morning

Half-time in blood (min)
Immediately after exposure

1.3

4.0

2.1

1.8

6.4

30 min after exposure

44

165

85

68

265

Next morning

129

223

220

443

317

11
Conclusion
The experimental data as well as PBPK simulations
suggest that sampling of blood or exhaled air is
appropriate.
However, sampling should not be carried out
immediately after shift, as the levels in blood and
exhaled air drop rapidly during the first minutes postexposure where after the decline is considerably
slower.
Read more ….
Ernstgård L, Sjögren B, Gunnare S, Johanson G. Blood and exhaled air can be used
for biomonitoring of hydrofluorocarbon exposure. Submitted to Toxicol Lett.

Ernstgård L, Sjögren B, Dekant W, Schmidt T, Johanson G. Uptake and disposition of 1,1difluoroethane (HFC-152a) in humans. Toxicol Lett. 2012 Feb 25;209(1):21-9.
Ernstgård L, Andersen M, Dekant W, Sjögren B, Johanson G. Experimental exposure to 1,1,1,3,3Pentafluoropropane (HFC-245fa): Uptake and disposition in humans. Toxicol Sci. 2010
Feb;113(2):326-36.
Gunnare S, Ernstgård L, Sjögren B, Johanson G. Experimental exposure to 1,1,1-trifluoroethane
(HFC-143a): uptake, disposition and acute effects in male volunteers.
Toxicol Lett. 2007 Aug;172(3):120-30
Gunnare S, Ernstgård L, Sjögren B, Johanson G. Toxicokinetics of 1,1,1,2-tetrafluoroethane
(HFC-134a) in male volunteers after experimental exposure. Toxicol Lett. 2006 Nov 1;167(1):5465.
Co workers
Bengt Sjögren
Sara Gunnare
Gunnar Johanson

Thank you for your attention!

Lena Ernstgård

14 oktober 2013

14

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2.4 Ernstgard

  • 1. Blood and exhaled air can be used for biomonitoring of hydrofluorocarbons in humans Lena Ernstgård Work environment toxicology, Institute of Environmental Medicine Karolinska Institutet, Sweden
  • 2. Introduction Various hydrofluorocarbons (HFCs) have replaced the ozone-depleting chlorofluorocarbons and hydrochlorofluorocarbons in refrigeration and air-conditioning applications. Colorless gases with faint, ethereal smell and are low-or non-flammable at atmospheric pressure and room temperature. Four studied HFCs; 1,1-Difluoroethane (HFC152a), 1,1,1trifluoroethane (HFC143a), 1,1,1,2-tetrafluoroethane (HFC134a), and 1,1,1,3,3-pentafluoropropane (HFC245fa).
  • 3. Aim The main objective of this study was to investigate the possibility to use blood and exhaled air for exposure biomonitoring of HFCs. Exposure to HFCs, e.g. during installation or repair of refrigeration or air-condition systems, occur as short peaks and probably locally distributed. Air monitoring in the breathing zone, may be misleading. In such cases, biological exposure monitoring may be advantageous as it more closely reflects the internal exposure.
  • 4. Method Exposures for 2 h at 50 W exercise. HFC152a (0, 500, and 1000 ppm) HFC143a (500 ppm) HFC134a (500 ppm) HFC245fa (0, 100, and 300 ppm) Sample collection 0-22 h postexposure: Capillary blood Exhaled air Urine Temperature 18°C and humidity 30% 4
  • 5. Methods Analysis of HFC in capillary blood, urine and exhaled air. By gas-chromatography The observed time courses in blood and exhaled air were described with a physiologically-based pharmacokinetic (PBPK) model. One model for all four HFC In additional PBPK simulations, the experimental 2-h exposures were extended to 8-h exposures to better capture occupational conditions. 5
  • 6. Partition coefficients Blood/air, and tissue/blood coefficients are essential to characterize the uptake and disposition of volatile substances. Experimental data on human blood:air, olive oil:air and water:air partition coefficients of all four HFCs and HFC125a (1,1,1,2,2pentafluoroethane). Ernstgård L, Lind B, Andersen ME, Johanson G. Liquid-air partition coefficients of 1,1-difluoroethane (HFC152a), 1,1,1-trifluoroethane (HFC143a), 1,1,1,2-tetrafluoroethane (HFC134a), 1,1,1,2,2pentafluoroethane (HFC125) and 1,1,1,3,3-pentafluoropropane (HFC245fa). J Appl Toxicol. 2010 Jan;30(1):59-62. 6
  • 7. PBPK model The PBPK parameters (compartmental volumes and blood flows and cardiac output) were calculated for each individual by allometric scaling based on body weight and height. Individually measured pulmonary ventilation rates, and chamber air concentrations. The parameters were also scaled to a 50-W workload or to rest. Sensitivity analyses showed that the blood:air partition coefficient is the most sensitive parameter.
  • 8. Results µM Blood. HFC152a (1000 ppm) 100 HFC143a (500 ppm) HFC134a (500 ppm) 10 HFC245fa (300 ppm) 1 Exposure 0.1 0 60 120 180 Time (min) 240 300 360 8
  • 9. Conc, µM 100 Conc, µM 100 B. 300 ppm HFC245fa A. 1000 ppm HFC152a 10 10 1 1 0.1 0.1 0.01 0.01 0 60 120 180 Time, min 240 300 0 360 60 120 180 240 300 360 Time, min Conc, µM Conc, µM 100 100 D. 500 ppm HFC134a C. 500 ppm HFC143a 10 10 1 1 0.1 0.1 0.01 0 60 120 180 240 300 360 0.01 0 Time, min Conc, µM 60 120 180 240 300 360 Time, min 100 E. 500 ppm HFC125a 10 1 0.1 0.01 0 60 120 180 240 Time, min 300 360 9
  • 10. Conc, µM HFC152a HFC245a HFC134a HFC143a HFC125a Blood 10 Conc, µM Blood 10 1 1 0.1 0.1 8,0 Time, h 8,5 0.01 0 2 4 6 Time, h 8 10 12 Exhaled air 10 Exhaled air Conc, µM Conc, µM 10 1 1 0.1 0.1 8,0 Time, h 8,5 0.01 0 2 4 6 Time, h 8 10 12 10
  • 11. HFC152a HFC143a HFC134a HFC245fa HFC125a Concentration in blood (µM) Immediately after exposure 11.7 2.3 4.8 7.7 1.4 30 min after exposure 3.8 0.61 1.4 2.4 0.33 0.0073 0.019 0.019 0.13 0.036 Next morning Concentration in exhaled air (µM) Immediately after exposure 3.8 1.1 2.1 3.0 0.65 30 min after exposure 1.2 0.28 0.59 0.87 0.16 0.0023 0.0089 0.0077 0.049 0.017 Next morning Half-time in blood (min) Immediately after exposure 1.3 4.0 2.1 1.8 6.4 30 min after exposure 44 165 85 68 265 Next morning 129 223 220 443 317 11
  • 12. Conclusion The experimental data as well as PBPK simulations suggest that sampling of blood or exhaled air is appropriate. However, sampling should not be carried out immediately after shift, as the levels in blood and exhaled air drop rapidly during the first minutes postexposure where after the decline is considerably slower.
  • 13. Read more …. Ernstgård L, Sjögren B, Gunnare S, Johanson G. Blood and exhaled air can be used for biomonitoring of hydrofluorocarbon exposure. Submitted to Toxicol Lett. Ernstgård L, Sjögren B, Dekant W, Schmidt T, Johanson G. Uptake and disposition of 1,1difluoroethane (HFC-152a) in humans. Toxicol Lett. 2012 Feb 25;209(1):21-9. Ernstgård L, Andersen M, Dekant W, Sjögren B, Johanson G. Experimental exposure to 1,1,1,3,3Pentafluoropropane (HFC-245fa): Uptake and disposition in humans. Toxicol Sci. 2010 Feb;113(2):326-36. Gunnare S, Ernstgård L, Sjögren B, Johanson G. Experimental exposure to 1,1,1-trifluoroethane (HFC-143a): uptake, disposition and acute effects in male volunteers. Toxicol Lett. 2007 Aug;172(3):120-30 Gunnare S, Ernstgård L, Sjögren B, Johanson G. Toxicokinetics of 1,1,1,2-tetrafluoroethane (HFC-134a) in male volunteers after experimental exposure. Toxicol Lett. 2006 Nov 1;167(1):5465.
  • 14. Co workers Bengt Sjögren Sara Gunnare Gunnar Johanson Thank you for your attention! Lena Ernstgård 14 oktober 2013 14