ナノ材料の有害性評価

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1 CRM CRM 181

2 TG424 TG TG407 PBPK PBPK DNA DNA

3 PBPK C C art vein Ramsey & Andersen (1984) ( Qalv Cinh Qt Cvein ) ( Qt Qalv PN ) = + + { ( )} Qi Ci = i Pi ( C ) art Ci dai dt = Qi Qt Pi ( C ) art Cl max ( Cl ) ( Cl ) = Q P + dal dt l V Pl Km Pl l GST P450 Q alv = Cinh = Qt = PN= Pi= Qi = V max KmMickaelis-Menten l=

4 PBPK AUC AUC Approaches for the Application of PBPK Models and Supporting Data in Risk Assessment (EPA/600/R-05/43A, June 2005, External Review Draft)

5 % DCM: B6C3F1 P450 GST AUC(DCM) (Andersen et al., 1987) GST AUC(DCM) DCM GST P450 GST mg DCM/liter tissue mg DCM/liter tissue ppm 250 a mg/kg/day b AUC(DCM) (mg/liter) x hr a NTP, 1986 b National Coffee Association, 1983

6 PBPK GST 1,4- DNA- AUC

7 TG424 TG TG407 PBPK PBPK DNA DNA

8 PBPK GST 1,4- * * * DNA-* AUC *

9 (Aplastic anemia), (acute myelogenous leukemia,aml) (lymphoid malignancies) Absolute lymphocyte count): : 5-19 ppm ---> () Ha-ras gene

10 Protein adducts DNA adducts P4502E1 Benzene O Benzene oxide Oxepin Fe/OH GSH O GSH-Transferase Epoxide hydrolase OH O [ O ] O O trans,trans -Muconaldehyde* OH (MUC) (highly reactive, hematotoxic, topoisomerase trans,trans-muconic acid (MA) (excreted in Urine: exposure marker in human) inhibition) OH S-CH 2 -CH(NHCOCH 3 )COOH S-Phenylmercapturic acid Glucuronide Sulfate P4502E1 HO Phenol OH HO Glucuronide Sulfate Hydroquinone* Protein adducts P450 DNA adducts OH Glucuronide OH OH 1,2,4-Benzene triol* P450 Catechol* NQO1 OH OH OH (polymorphism) 1,2-Benzene dihydrodiol* Peroxidases/autooxidation (Myeloperoxidase: MPO) *:mutagenic NQO1? Protein adducts O O O O o-benzoquinone O O Protein adducts NQO1 4,4'-Diphenoquinone p-benzoquinone (highly reactive, oxidative stress, topoisomerase inhibition, inhibits pre-il-1 to IL-1) OH OH 4,4'-Biphenol NQO1: NAD(P)H:quinone oxidoreductase

11 (U.S.EPA, 2002) CYP2E1 GSH transferases >> NAD(P)H:quinone oxidoreductase CYP2E1xNQO1 CYP2E1 NQO1 (95% CI) ( ) ( ) ( )

12 > >

13 EU / WHO-IPCS The Sapphire Group U.S. EPA WHO Canada TERA European Risk Assessment Report, ACRYLONITRILE (Final Report, 2004) Environmental Health Criteria 28, Acrylonitrile (1983) Toxicological Review of Acrylonitrile (Final Draft, 2004) TOXICOLOGICAL PROFILE FOR ACRYLONITRILE, 1990 Concise International Chemical Assessment Document 39, ACRYLONITRILE (2002) Priority Substances List Assessment Report Acrylonitrile (2000) Acrylonitrile: Inhalation Cancer Risk Assessment (1997)

14 U.S. EPA NICNAS WHO / Ambient Water Quality Criteria for the Protection of Human Health: Acrylonitrile (1998) Acrylonitrile Priority Existing Chemical Assessment Report No. 10 ( 2000) Air quality Guidelines for Europe, Second Edition, Chapter 5.1 Acrylonitrile (2000) Chronic Toxicity Summary, ACRYLONITRILE(2001)

15 IARC BUA ECB ATSDR NICNAS EPA CANADA CRM

16 CRM (a) (b) (c) CRM CRM

17 NOAEL 2004 The Sapphire 2004 Group, Inc. The California Saophire OEHHA Group, Inc. 2 x 10-3 mg/m 3 (UF=500) RfD=0.2 mg/kg/ (UF=180) RfC=0.7 mg/m 3 (UF=10) Cancer Value = 0.1 mg/m 3 RfC5 x 10-3 mg/m 3 (UF=30) Cancer Value = mg/kg/ NOEL 1 mg/m 3 (Muto et al., 1992) NOAEL 32 mg/kg// NOAEL 21.7 mg/m 3 NOAEL( 7.4 mg/m 3 BMD 05 (Maltoni et al., 3.3 mg/m 1977,1987; Toxicology 3 BMD Research Laboratory, ; Johannsen and 0.15 mg/m Levinskas, 2002a; b; Quast, 2002) in vivo 5/7 PBPKNOAELBMD (Gagnaire et al., 1998) LED 1SD = NOAEL NOAEL(21.7 mg/m 3 ) (10 m 3 /day20 m 3 /)250/ (Sakurai et CEOBMD5% al., 1978) 365/ (LED 05 )(0.014 mg/l) NOAEL(7.4 mg/m 3 ) Point of Departure (POD) POD CEOKedderis PBPK(21.3 mg/m 3 ) et al. (1996)PBPK UF=220 BMD5%BMD Toxicology Research 05 ) (3.3 mg/m Laboratory, 1980) 3 ) Cancer Value CEOMD5% (0.15 mg/m 3 )UF=305 x 10-3 mg/m 3 (LED 05 )(0.014 mg/l) Point of Departure (POD) POD PBPK(1.7 mg/kg/) UF=200 WHO 2002 TC 05 = 6.0 mg/m 3 95%LCL = 4.5mg/m x 10-2 / (mg/m 3 ) TD 05 = 2.3 mg/kg/ (95%LCL = 1.4 mg/kg/) 2.2 x 10-2 / (mg/kg/) Toxicology Research Laboratory, 1980) (Johannsen and Levinskas, 2002b) 6 TC 05 TC 05 =35 mg/m 3 ()52 mg/m 3 24 [(6hr/)/(24hr/)] x [(5 /)/(7 /)] TC 05 TC 05 TD 05 =2.0 mg/kg/() 1.8 mg/kg/() TD 05 () x (26/24) x (26/24) 2

18 (U.S. EPA, 1998) EU (2004) The Sapphaire Group, Inc. (2004) NOAEL RfD= 1 g/kg/ RfD=200 g/kg/ 1 mg/kg/ 0.25 mg/kg/ 32 mg/kg/ (Tandon et al. 1988) (Johannsen and Levinskas, 2002 (Gagnaire et al., 1998) UF=1,000 PBPKNOAEL UF=180TERA PBPK PBPK Gagnaire et al.(1998) (ASAP) ASAP) BMDNOAEL

19 (ASAP) 5/ mg/kg/ (7/) mg/kg/ ASAP (V) MeanS.D (n=10) (n=12) (n=12) (n=12) BMD BMD (mg/kg/) BMDL (mg/kg/) p Linear Polynomial Power Hill BMDBMDL:BMD95% RfD = 20g/kg/ g/kg/

20 (U.S. EPA, 1998) EU (2004) The Sapphaire Group, Inc. (2004) CRM NOAEL RfD=1 g/kg/ RfD=200 g/kg/ RfD =20 g/kg/ 1 mg/kg/ 0.25 mg/kg/ 32 mg/kg/ 20 mg/kg/ (Tandon et al. 1988) (Johannsen and Levinskas, 2002 (Gagnaire et al., 1998) (Gagnaire et al., 1998) UF=1,000 PBPKNOAEL UF=180 TERA BMDNOAEL UF=1,000

21 CRM / EU European Risk Assessment Report (2004) WHO-IPCS Environmental Health Criteria 28 (1983) The Sapphire Group Toxicological Review (Final Draft, 2004) U.S. EPA Toxicological Profile (1990) WHO Canada Concise International Chemical Assessment Document 39 (2002) Priority Substances List Assessment Report (2000) CRM NICNAS Priority Existing Chemical Assessment Report No. 10 ( 2000) 64 62

22 PBPK

23

24 P450 2E1 MOF GSTH (+) GSH (-) ) (-) 0.25, 0.2, 0.02) 75, 5, 5)

25 / Ca

26

27 PBPK

CAS O C O * DOP* DEHP 2- C O O * n- C 24 H 38 O CH 2 CH 2 CH 2 CH 3 CH (CH 2 ) % 2- A BHT , 4

CAS O C O * DOP* DEHP 2- C O O * n- C 24 H 38 O CH 2 CH 2 CH 2 CH 3 CH (CH 2 ) % 2- A BHT , 4 2-1 9628 31307 CAS 117817 2- O C O * DOP* DEHP 2- C O O * n- C 24 H 38 O 4 390.56 CH 2 CH 2 CH 2 CH 3 CH (CH 2 ) 3 1 99 % 2- ABHT 1. 2-55 3 3, 4 386 171 350 6 0.1 % d 20 4 0.9861 4 13.48 0.30410-4 Pa 2.2810-7

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