superfund advisory committee january 23, 2014 tetrachloroethylene: cancer risk values office of...

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erfund Advisory Committee January 23, 2 Tetrachloroethylene: Cancer Risk Values Office of Research and Standards Sandra Baird, Ph.D. 1

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Superfund Advisory Committee January 23, 2014

Tetrachloroethylene:Cancer Risk Values

Office of Research and Standards

Sandra Baird, Ph.D.

1

Road Map

2

Brief History

2012 US EPA final based on liver tumorsDerived values for leukemia and liver

• 2008 MassDEP based on leukemia and liver• 2008 US EPA draft based on leukemia• 2010 NRC Review lacked consensus on

leukemia• 2011 US EPA Interagency draft based on

leukemia

3

Why did we review PCE?

• Basis of US EPA 2012 value different from – MassDEP’s 2008 and 1990– US EPA 2008 and 2011

• NRC Committee did not reach consensus• US EPA 2012 two IURs >10-fold different• US EPA 2012 liver-based IUR differed

substantially from US EPA 2008 liver and leukemia-based IUR

4

ORS Process

• Review recent data, primary literature, models• MassDEP Health Effects Advisory Committee• Authors of US EPA Harmonized PBPK model• Address concerns from NRC & interested parties– High leukemia background rate– Dose response– NTP data– Relevance to humans– Up to date PBPK model

5

Decisions

• US EPA harmonized PBPK model should be used

• JISA 1993 bioassay should be used not NTP 1986

• Leukemia data should be used to derive PCE cancer risk values

• Total metabolized PCE should be used for interspecies extrapolation instead of total PCE

6

Leukemia Endpoint

• Background rate high but…– Treated animal rate higher

• Earlier and more severe in treated animals• Statistically significant dose-response

NTP & JISA• No data to rule out relevance to humans

7

Derivation

• JISA 1993 (0, 50, 200, 600 ppm)• Males and Female Rats• Harmonized PBPK model• Total Metabolized Dose

8

Cancer Risk Values

• Inhalation and oral values are based on same extrapolation from inhalation studies

• Inhalation unit risk (IUR)3 x 10-6 per ug/m3

• Oral cancer slope factor (CSF)2 x 10-2 per mg/kg/day

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Method 3 Short-Form

2008-2012 2014

Unit Risk (per ug/m3) 1 x 10-5 3 x 10-6

Residential (ug/m3)

No Significant Risk (NSR) 2 8Imminent Hazard (IH) 10 50Workplace (ug/m3)

No Significant Risk (NSR) 10 40Imminent Hazard (IH) 60 200

10

RiskConc.

Back-ground

Ind

oor

Air

Con

cen

trati

on

(u

g/m

3)

TargetAir

Conc.

RiskConc.

Back-ground

DEP pre-2008 Tox Value DEP 2014 Tox Value

Proposed Target Indoor Air Concentration and GW-2 Standard

TargetAir

Conc.

GW-2 = 50 ug/L GW-2 = 20 ug/L

5

10

0.04

11 11

0.2

4 4

15

11

Thank You!

More information on tetrachloroethylene cancer risk values will be posted on MassDEP Chemical page

http://www.mass.gov/eea/agencies/massdep/toxics/sources/chemical-research-and-standards.html

Questions? Comments?

[email protected]

12

13

RiskConc.

Back-ground

Ind

oor

Air

Con

cen

trati

on

(u

g/m

3)

TargetAir

Conc.

RiskConc.

Back-ground

DEP pre-2008 Tox Value DEP 2014 Tox Value

Proposed Target Indoor Air Concentration and GW-2 Standard

TargetAir

Conc.

GW-2 = 50 ug/L GW-2 = 20 ug/L

5

10

0.04

11 11

0.2

4 4

15

RiskConc.

Back-ground

US EPA 2012 Tox Value

TargetAir

Conc.

GW-2 = 30 ug/L

7.8

4

8

14

Method 3 Short-Form

2008-2012 2014 US EPA

Unit Risk (per u/m3) 1 x 10-5 3 x 10-6 3 x 10-7

Residential (u/m3)No Significant Risk (NSR) 2 8 40Imminent Hazard (IH) 10 50 400

Workplace (u/m3)No Significant Risk (NSR) 10 40 180Imminent Hazard (IH) 60 200 1800

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