Chapter 14
Dermal Absorption and Pharmacokinetics of Pesticides in Rats 1
2
3
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P. V. Shah , H. L. Fisher , M . R. Sumler , and L. L. Hall
2
1Toxic Effects Branch, Health and Environmental Review Division (TS-796), Office of Toxic Substances, U.S. Environmental Protection Agency, Washington, DC 20460 Cellular Biology Branch, Health Effects Research Laboratory, U.S. Environmental Protection Agency, Research Triangle Park, NC 27711 Northrop Environmental Sciences, Northrop Corporation, Research Triangle Park, NC 27709 2
3
Dermal a b s o r p t i o n and d i s p o s i t i o n o f carbaryl, c a r b o f u r a n , c h l o r d e c o n e , h e x a c h l o r o b i p h e n y l and d i n o s e b were s t u d i e d in female F i s c h e r 344 rats. Acetone s o l u t i o n o f t h e [14C] l a b e l e d pesticide was a p p l i e d to a p r e v i o u s l y c l i p p e d m i d - d o r s a l r e g i o n o f t h e back. At v a r i o u s t i m e i n t e r v a l s , a n i m a l s were killed and s e l e c t e d organs were a n a l y z e d f o r radioactive [14C] c o n t e n t . A physiological compartmental model was f i t t e d t o t h e s k i n p e n e t r a t i o n , tissue distribution, and e x c r e t i o n d a t a . The e q u i l i b r i u m t i s s u e t o b l o o d ratios and excretion r a t e c o n s t a n t s and s k i n a b s o r p t i o n rate were d e t e r m i n e d f r o m t h e model. In many c a s e s , differences in kinetics and retention were found between young and a d u l t rats. The dermal p e n e t r a t i o n function was s i n g l e o r biexponential, requiring a one o r two compartmental model f o r s i m u l a t i n g t h e s k i n penetration process. More t h a n one b i l l i o n pounds o f p e s t i c i d e s a r e b e i n g u s e d each year i n the U n i t e d S t a t e s alone t o i n c r e a s e the p r o d u c t i v i t y of a g r i c u l t u r a l l a n d ( 1 ) . G r e a t e r r e l i a n c e on use o f p e s t i c i d e s appears i n e v i t a b l e as t h e demand f o r f o o d p r o d u c t i o n i n c r e a s e s w i t h i n c r e a s i n g p o p u l a t i o n . O c c u p a t i o n a l exposure t o p e s t i c i d e s o c c u r s v i a o r a l , d e r m a l , and i n h a l a t i o n r o u t e s . A l t h o u g h t h e r a t e o f a b s o r p t i o n may be h i g h e r by pulmonary and o r a l r o u t e s , t h e t o t a l amount absorbed a f t e r s k i n c o n t a c t may be much g r e a t e r d u r i n g o c c u p a t i o n a l exposure t o p e s t i c i d e s (2,3). Knowledge of dermal a b s o r p t i o n ( r a t e s and e x t e n t ) o f p e s t i c i d e s i s v e r y i m p o r t a n t i n r i s k assessment and e s t a b l i s h m e n t 0097-6156/89/0382-0169$06.00/0 ° 1989 American Chemical Society
Wang et al.; Biological Monitoring for Pesticide Exposure ACS Symposium Series; American Chemical Society: Washington, DC, 1988.
170
BIOLOGICAL MONITORING FOR PESTICIDE EXPOSURE
of r e e n t r y standards f o r f i e l d workers. With r e g a r d t o o c c u p a t i o n a l e x p o s u r e t o t o x i c a n t s i n g e n e r a l , r i s k assessment has u s u a l l y been b a s e d on s t u d i e s i n a d u l t s . S k i n a b s o r p t i o n depends on a number o f f a c t o r s , i n c l u d i n g t h e c h e m i c a l and p h y s i c a l n a t u r e o f t h e p e n e t r a n t and t y p e o f s k i n . The l i m i t e d l i t e r a t u r e on t h e e f f e c t s o f age on s k i n p e n e t r a t i o n has been r e c e n t l y summarized (4)» I t a p p e a r s t h a t t h e e f f e c t o f age on p e r c u t a n e o u s a b s o r p t i o n v a r i e s w i t h s p e c i e s , compound, and method o f assessment. I n c r e a s e d s k i n p e r m e a b i l i t y o f n e o s y n e p h r i n e (as measured by t h e b l a n c h i n g r e s p o n s e ) i n p r e m a t u r e i n f a n t s compared t o f u l l t e r m i n f a n t s has been documented (50. No d i f f e r e n c e s i n p e r c u t a n e o u s a b s o r p t i o n o f t e s t o s t e r o n e between t h e newborn and a d u l t r h e s u s monkey was n o t e d {6J, w h i l e more r a p i d l o s s o f t o p i c a l l y a p p l i e d t r i a d i m e f o n from t h e s k i n o f young Sprague-Dawley r a t s has been r e p o r t e d (7). A recent c o m p a r a t i v e s t u d y on p e r c u t a n e o u s a b s o r p t i o n o f p e s t i c i d e s i n young and a d u l t F i s c h e r 344 r a t s r e p o r t e d age-dependent p e r c u t a n e o u s a b s o r p t i o n f o r 11 o u t o f 14 p e s t i c i d e s s t u d i e d (8) • We p r e s e n t h e r e t h e c o m p a r a t i v e p e r c u t a n e o u s a b s o r p t i o n and d i s p o s i t i o n of c a r b a r y l , carbofuran, chlordecone, hexachlorob i p h e n y l , and d i n o s e b i n young and a d u l t F i s c h e r 344 r a t s u t i l i z i n g i d e n t i c a l methodology. A l s o , comparison o f t h e r e s u l t s o f i n v i v o and two i n v i t r o methods f o r p e r c u t a n e o u s a b s o r p t i o n measurements a r e p r e s e n t e d . The u t i l i t y o f t h e p h y s i o l o g i c a l compartmental model i n s i m u l a t i n g dermal a b s o r p t i o n and disposition i s discussed. EXPERIMENTAL APPROACH; CHEMICALS The c h e m i c a l s s t u d i e d , t h e i r r e s p e c t i v e s p e c i f i c a c t i v i t i e s , r a d i o l a b e l i n g p o s i t i o n , and s o u r c e s a r e l i s t e d i n T a b l e I . The r a d i o c h e m i c a l p u r i t y was g r e a t e r t h a n 98% f o r a l l pesticides studied. U n l a b e l e d c h e m i c a l s were s u p p l i e d by t h e P e s t i c i d e and I n d u s t r i a l C h e m i c a l R e p o s i t o r y (U.S. E n v i r o n m e n t a l P r o t e c t i o n Agency, R e s e a r c h T r i a n g l e Park, NC). Minimum E s s e n t i a l Medium (MEM) E a g l e Formula w i t h E a r l ' s s a l t s a n d L - g l u t a m i n e and w i t h o u t p h e n o l r e d and sodium c a r b o n a t e was p u r c h a s e d from G i b c o L a b o r a t o r i e s , C h a g r i n F a l l s , OH. HEPES ( N- 2h y d r o x y e t h y l p i p e r a z i n e - N - 2 - e t h a n e s u l f o n i c a c i d ) , sodium p y r u v a t e , L- s e r i n e , L - a s p a r t i c a c i d , and g e n t a m i c i n were p u r c h a s e d from G i b c o , Grand I s l a n d , NY. Anhydrous sodium c a r b o n a t e , sodium h y d r o x i d e , e t h y l e t h e r ( a n h y d r o u s ) , and a c e t o n e ( r e a g e n t grade) were p u r c h a s e d from F i s h e r S c i e n t i f i c Co., F a i r l a w n , NJ. IN VIVO APPLICATION Female F i s c h e r 344 r a t s o f 33 (young) and 82 ( a d u l t ) days o f age were u t i l i z e d f o r d e r m a l a b s o r p t i o n e x p e r i m e n t s . Three r a t s were u s e d f o r each t i m e p o i n t . Randomized o f f s p r i n g f r o m t i m e d p r e g n a n t r a t s were u s e d i n o r d e r t o have b e t t e r c o n t r o l o v e r t h e age and w e i g h t o f t h e a n i m a l s u s e d i n t h e s e e x p e r i m e n t s . The i n v i v o e x p e r i m e n t a l t e c h n i q u e s employed i n t h i s s t u d y have been d e s c r i b e d i n d e t a i l by Shah e t a l . ( 8 ) .
Wang et al.; Biological Monitoring for Pesticide Exposure ACS Symposium Series; American Chemical Society: Washington, DC, 1988.
Wang et al.; Biological Monitoring for Pesticide Exposure ACS Symposium Series; American Chemical Society: Washington, DC, 1988. position
C
C
,
,
Klng(U)
Ring(U)
,
1
4
C C £ / ;
]
Benzofuranyl r i n g
2 , 4 , 5 , 2 , 4 , 5 - [
1 4
1 4
^^C(U)
1 4
Naphthyl[1- C]
Radiolabeling
2,4,5,2*,4',5'-Hexachlorobiphenyl.
9.2
4.29
Dinoseb
1
3.2
Chlordecone
PCB
39.4
5.8
Carbofuran
Carbaryl
Specific activity (mCi/mM)
New E n g l a n d N u c l e a r , B o s t o n , MA
P a t h f i n d e r Lab., I n c . , S t . L o u i s , MO
Midwest R e s e a r c h I n s t i t u t e , Kansas C i t y , MO
FMC Corp., P r i n c e t o n , NJ
Amersham, A r l i n g t o n H e i g h t s , I L
Source
P e s t i c i d e s T e s t e d i n P r e s e n t S t u d y , w i t h S p e c i f i c A c t i v i t y , R a d i o l a b e l i n g P o s i t i o n , and Source
Common name
TABLE I .
172
BIOLOGICAL MONITORING FOR PESTICIDE EXPOSURE
B r i e f l y , t h e a n i m a l ' s h a i r was c l i p p e d 24 h p r i o r t o dermal a p p l i c a t i o n w i t h O s t e r a n i m a l h a i r c l i p p e r s ( O s t e r , Milwaukee, WI). D o s i n g s o l u t i o n s (0.1 mL young and 0.2 mL a d u l t ) c o n t a i n i n g r a d i o a c t i v i t y and a p p r o p r i a t e dose (285 nmol/cm ) i n a c e t o n e were a p p l i e d t o t h e p r e v i o u s l y c l i p p e d mid-back r e g i o n o f t h e r a t . The t r e a t e d a r e a , w h i c h r e p r e s e n t s a p p r o x i m a t e l y 2.3% o f t h e t o t a l body s u r f a c e a r e a (2.8 cm young , 5.6 cm a d u l t ) , was p r o t e c t e d f r o m grooming by p l a c i n g a n o n o c c l u s i v e d e v i c e o v e r i t . At t h e end o f the d e s i g n a t e d t i m e i n t e r v a l , the a n i m a l was a n e s t h e t i z e d w i t h e t h e r and a b l o o d specimen was o b t a i n e d from t h e h e a r t . V a r i o u s t i s s u e s were removed t o determine t h e d i s t r i b u t i o n o f dermally absorbed r a d i o - l a b e l e d p e s t i c i d e s . A l l t h e t i s s u e s , e x c r e t o r y p r o d u c t s , and c a r c a s s e s were a n a l y z e d f o r r a d i o a c t i v i t y by l i q u i d s c i n t i l l a t i o n c o u n t i n g as d e s c r i b e d by Shah e t a l . ( 8 ) . 2
2
2
IN VITRO PROCEDURE I n v i t r o a b s o r p t i o n o f p e s t i c i d e s t h r o u g h young and a d u l t s k i n was d e t e r m i n e d by u s i n g b o t h F r a n z c e l l s and c o n t i n u o u s flow-through cells. The d e t a i l e d e x p e r i m e n t a l and s k i n p r e p a r a t i o n t e c h n i q u e s have been d e s c r i b e d i n d e t a i l by Shah e t a l . (_9). B r i e f l y , back h a i r was c l i p p e d 24 h p r i o r t o e x p e r i m e n t . A n i m a l s were k i l l e d w i t h c a r b o n d i o x i d e , and back s k i n was c a r e f u l l y e x c i s e d . Skin was f l o a t e d on t i s s u e c u l t u r e medium (minimum e s s e n t i a l media, Eagle formula w i t h E a r l ' s S a l t s ) . S p l i t t h i c k n e s s (350 um t h i c k n e s s ) s k i n s o b t a i n e d w i t h a dermatome ( P a d g e t t Dermatome, Kansas C i t y , MO) were mounted i n t h e i n v i t r o c e l l s w i t h e p i d e r m i s exposed t o t h e e n v i r o n m e n t . Only one s k i n d i s c was used from each animal. The amount o f p e s t i c i d e ( i n a c e t o n e ) per cm a r e a was k e p t t h e same f o r b o t h i n v i v o and i n v i t r o e x p e r i m e n t s . Receptor f l u i d was m a n u a l l y removed p e r i o d i c a l l y from t h e F r a n z c e l l s t o d e t e r m i n e t h e r a t e and e x t e n t o f p e n e t r a t i o n , w h i l e c o n t i n o u s f l o w t h r o u g h c e l l s w i t h a media f l o w r a t e of 3 mL/h were a u t o m a t i c a l l y sampled every 3 h. Sample p r e p a r a t i o n f o r r a d i o a c t i v i t y d e t e r m i n a t i o n and o x i d a t i o n o f t r e a t e d s k i n were done a c c o r d i n g t o p r o c e d u r e d e s c r i b e d by Shah e t a l . (8_). B r i e f l y , t h e t r e a t e d s k i n was combusted i n t h e sample o x i d i z e r t o measure the r e m a i n i n g r a d i o a c t i v i t y i n o r on t h e s k i n . A l l o t h e r samples were mixed w i t h 10 mL I n s t a - G e l ( P a c k a r d I n s t r u m e n t Co., Downers Grove, I L ) for s c i n t i l l a t i o n counting. 2
Data A n a l y s i s S t a t i s t i c a l c o m p a r i s o n s t o d e t e r m i n e t h e e f f e c t o f age on s k i n p e n e t r a t i o n of p e s t i c i d e s were made u s i n g t h e S t a t i s t i c a l A n a l y s i s System package (10) w i t h age and age X t i m e as c l a s s v a r i a b l e s i n the g e n e r a l l i n e a r model (GLM). R e c i p r o c a l v a r i a n c e was used f o r weighting. The s i g n i f i c a n c e o f t h e l a b o r a t o r y method u s e d ( f l o w , s t a t i c , i n v i v o ) was d e t e r m i n e d w i t h t h e SAS u s i n g age, method, and age X method, and age X method X t i m e as c l a s s v a r i a b l e s i n the GLM and r e c i p r o c a l v a r i a n c e f o r w e i g h t i n g .
Wang et al.; Biological Monitoring for Pesticide Exposure ACS Symposium Series; American Chemical Society: Washington, DC, 1988.
14.
SHAH ET AL.
Absorption and Pharmacokinetics
173
A m a t h e m a t i c a l model was c o n s t r u c t e d a l o n g t h e l i n e s o f t h e p h y s i o l o g i c a l model d e v e l o p e d by Bungay e t a l . (11,12). L e a s t squares f i t t i n g o f t h e model t o t h e d a t a was done u s i n g SAAM 27, a computer package d e v e l o p e d a t t h e N a t i o n a l I n s t i t u t e s o f H e a l t h (NIH) by Berman and Weiss ( 1 3 ) . RESULTS S k i n a b s o r p t i o n o f c a r b o f u r a n as d e t e r m i n e d by t h e t h r e e methods i s shown i n T a b l e I I . The i n v i v o s k i n a b s o r p t i o n o f c a r b o f u r a n was 4.7% a t 6 h and 33.5% a t 72 h i n young a n i m a l s . I n a d u l t s , i t i n c r e a s e d from 2.0% a t 6 h t o 11.8% a t t h e 72 h t i m e p o i n t . The s t a t i c system gave 3.1% s k i n a b s o r p t i o n a t 6 h and 12.0% a t 72 h i n young a n i m a l s , w h i l e i n a d u l t s , a b s o r p t i o n ranged from 1.7% a t 6 h t o 8.8% a t t h e 72 h t i m e p o i n t . The s k i n a b s o r p t i o n o f c a r b o f u r a n as d e t e r m i n e d by t h e f l o w system i n young a n i m a l s ranged from 27.3% a t t h e 6 h t o 41.1% a t 72 h t i m e p o i n t . I n a d u l t s , i t ranged from 5.0% a t 6 h t o 11.2% a t t h e 72 h t i m e p o i n t . The y o u n g / a d u l t r a t i o o f s k i n p e n e t r a t i o n a t 72 h was 2.9 ( i n v i v o ) , 3.7 ( f l o w ) , and 1.4 ( s t a t i c ) . Thus, a l l t h r e e methods gave h i g h e r s k i n p e n e t r a t i o n v a l u e s i n young r a t s compared t o a d u l t s . However, t h e s t a t i c c e l l gave c o n s i s t e n t l y l o w e r s k i n p e n e t r a t i o n v a l u e s i n young r a t s compared t o i n v i v o o b s e r v a t i o n s . S k i n a b s o r p t i o n o f c a r b a r y l as d e t e r m i n e d by t h e t h r e e methods i s shown i n T a b l e I I I . The s k i n a b s o r p t i o n o f c a r b a r y l ( i n v i v o ) ranged from 2.4% a t 6 h t o 38.5% a t 72 h i n young a n i m a l s , and i n a d u l t s i t ranged from 3.6% a t 6 h t o 38.4% a t 72 h. The s k i n a b s o r p t i o n o f c a r b a r y l ( s t a t i c ) ranged from 5.3% a t 6 h t o 20.9% a t 72 h i n t h e young, and i n a d u l t s , i t ranged from 4.7% a t 6 h t o 20.3% a t 72 h. The s k i n a b s o r p t i o n o f c a r b a r y l ( f l o w ) ranged from 18.8% a t 6 h t o 29.2% a t 72 h i n young a n i m a l s , and i n a d u l t s , i t ranged from 8.1% a t 6 h t o 18.2% a t 72 h. Both i n v i v o and s t a t i c systems showed no s i g n i f i c a n t y o u n g / a d u l t d i f f e r e n c e s i n s k i n p e n e t r a t i o n o f c a r b a r y l a t t h e 72 h t i m e p o i n t , w h i l e t h e f l o w system gave s i g n i f i c a n t d i f f e r e n c e s i n s k i n p e n e t r a t i o n between young and a d u l t a n i m a l s , w i t h young a b s o r b i n g more c a r b a r y l compared t o a d u l t s . S k i n a b s o r p t i o n o f d i n o s e b as d e t e r m i n e d by t h e t h r e e methods i s shown i n T a b l e IV. Dinoseb showed r a p i d p e n e t r a t i o n i n b o t h young and a d u l t r a t s compared t o o t h e r p e s t i c i d e s . The r e s u l t s from t h e i n v i v o method showed a s t a t i s t i c a l l y s i g n i f i c a n t l o w e r s k i n a b s o r p t i o n o f d i n o s e b i n young a n i m a l s . In t h e young, s k i n a b s o r p t i o n ranged from 11.1% a t 1 h t o 55.7% a t 72 h, w h i l e i n a d u l t s , i t ranged from 22.3% a t 1 h t o 84.3% a t 72 h. The s t a t i c method i n d i c a t e s s i g n i f i c a n t d i f f e r e n c e s i n s k i n p e n e t r a t i o n o f d i n o s e b i n young and a d u l t , e x c e p t a t 1 h s a m p l i n g p e r i o d . In the young, t h e s k i n a b s o r p t i o n v a l u e ( s t a t i c ) , f o r d i n o s e b ranged from 3.0% a t 1 h t o 74.9% a t 72 h, and i n t h e a d u l t , i t ranged from 1.5% a t 1 h t o 70.8% a t 72 h. The f l o w system i n d i c a t e d s i g n i f i c a n t young/adult d i f f e r e n c e s i n s k i n absorption of dinoseb a t a l l t i m e p o i n t s , and young a b s o r b e d more t h a n t w i c e t h e amount o f d i n o s e b as a d u l t s . The s k i n a b s o r p t i o n v a l u e ( f l o w ) i n young ranged from 6.4% a t 1 h t o 47.3% a t 72 h, and 2.4% a t 1 h t o 20.6% a t 72 h i n t h e a d u l t .
Wang et al.; Biological Monitoring for Pesticide Exposure ACS Symposium Series; American Chemical Society: Washington, DC, 1988.
Wang et al.; Biological Monitoring for Pesticide Exposure ACS Symposium Series; American Chemical Society: Washington, DC, 1988.
11.2±0.9
3.7**
4. 1**
NS
f o r the hypothesis
0.05.
S i g n i f i c a n t a t p < 0.05
from J . T o x i c o l . E n v i r o n .
NS Not s i g n i f i c a n t , p >
**
* Reprinted
Age X t i m e
Health.
12.0±1.1
9.8±1.0
7.0±0.8
8.8±0.8
7.1±0.7
4.6±0.5
1.7±0.2
o f no y o u n g - a d u l t d i f f e r e n c e .
22:207-223, 1987 w i t h p e r m i s s i o n
of publisher.
o
w w
o
H O
o •* *•
P 3E
o 5
s
**
2.9**
3.8**
4.2**
2.4
Young adult
**
11.8±0.9
6.8±0.1
5.7±1.2
2.0±0.2
Adult
In v i v o
o H o 2
33.5±2.7
26.1±2.6
23.9±1.8
4.7±0.7
Young
Carbofuran*
3.4**
1.4**
1.4**
1.5**
1.8
Young/ adult
**
41.1±5.9
72
9.7±0.9
4.6**
3.1±0.5
Adult
Age
39.4±6.0
48
7.8±0.9
5.5**
Young
1.4**
36.0±5.7
24
5.0±0.6
Young/ adult
System
Penetration
Static
% Skin
Comparison o f S k i n P e n e t r a t i o n o f
4.3**
27.3±4.5
6
Adult
Methods
All
Young
Time (h)
Flow System
TABLE I I .
Wang et al.; Biological Monitoring for Pesticide Exposure ACS Symposium Series; American Chemical Society: Washington, DC, 1988.
S i g n i f i c a n t a t p < 0.05 f o r t h e h y p o t h e s i s Not s i g n i f i c a n t , p > 0.05.
o f no y o u n g - a d u l t
difference.
*
*
Age X Time
* NS
NS
1.04
1.03
*
20.3±1.9
1.02
1.02
1.15
Age
20.9±1.5
16.1±1.6
11.1±1.1
4.7±0.6
Young Adult
1.80*
1.60*
System
Adult
Static
Penetration
All
18.2±2.6
29 2±2.9
72
16.5±1.2
1.70*
16.0±2.3
27 2±2.8
48
11.4±0.8
1.86*
13.3±1.9
24 6±2.6
24
5.3±0.5
2.33*
8.1±1.2
Young
Adult
18 .8±2.1
Young
6
Time (h)
Young Adult
Flow System
% Skin
38.5±2.4
23.6±1.0
14.9±2.5
2.4±0.3
Young
TABLE I I I . Methods Comparison o f S k i n P e n e t r a t i o n o f C a r b a r y l
Adult
Vivo
38.4±1.3
32.4±0.7
15.2±1.2
3.6±0.5
In
*
*
0.89*
1.00
0.73*
0.98
0.66*
Young Adult
Wang et al.; Biological Monitoring for Pesticide Exposure ACS Symposium Series; American Chemical Society: Washington, DC, 1988.
29.0±3.5
41.0±3.7
45.0±3.8
47.3±3.9
6
24
48
72
20.6±3.5
18.6±3.0
15.7±2.5
11.19±2.2
2.4±0.6
Flow System Adult
0.70*
0.66*
difference.
*
84.3±2.7
0.65*
*
55.7±2.4
85.1±1.9
55.3±9.7
*
1.10
1.06
1.07
0.74*
0.90
43.1±9.4 85.5±1.8
0.50 22.3±8.8
In V i v o Ratio Adult
63.0±2.9
38.8±5.7
11.1±2.1
Young
*
70.8±3.8
66.2±3.8
1.13
1.22
17.0±1.1 52.3±3.1
2.00*
1.5±0.1
S t a t i c System Adult Ratio
*
74.9±8.0
70.9±8.4
59.1±7.4
20.7±2.0
3.0±0.2
Young
*
2.47*
2.29*
2.42*
2.62*
2.61*
2.64*
Ratio
Penetration
* S i g n i f i c a n t a t p < 0.05 f o r t h e h y p o t h e s i s o f no y o u n g - a d u l t
Age X Time
Age
All
6.4±1.0
1
\
Youna
Time (h)
% Skin
TABLE IV. Methods Comparison o f S k i n P e n e t r a t i o n o f Dinoseb
0
6
a
O
W
5
H
Gfl
W
o 2 2 o *i o
H
o
1
5
14.
Absorption and Pharmacokinetics
SHAH ET AL.
177
Methods c o m p a r i s o n o f h e x a c h l o r o b i p h e n y l s k i n p e n e t r a t i o n i n young and a d u l t r a t s i s shown i n T a b l e V. I n v i t r o s k i n a b s o r p t i o n v a l u e s o f h e x a c h l o r o b i p h e n y l i n young and a d u l t r a t s were s i g n i f i c a n t l y lower t h a n i n v i v o r e s u l t s . Skin absorption v a l u e s i n young a t 6 h were 0.012%, 0.071%, and 2.5% as d e t e r m i n e d by f l o w , s t a t i c , and i n v i v o methods, r e s p e c t i v e l y . In a d u l t s , s k i n a b s o r p t i o n v a l u e s a t 6 h were 0.015, 0.019, and 0.63% as d e t e r m i n e d by f l o w , s t a t i c , and i n v i v o methods, r e s p e c t i v e l y . S k i n a b s o r p t i o n v a l u e s i n young a t 72 h were 1.25, 2.50, and 33.2% as d e t e r m i n e d by f l o w , s t a t i c and i n v i v o methods, r e s p e c t i v e l y . In a d u l t s , 72 h s k i n a b s o r p t i o n v a l u e s were 1.36, 1.15, and 19.6% as d e t e r m i n e d by f l o w , s t a t i c and i n v i v o methods, r e s p e c t i v e l y . Both i n v i t r o methods showed n o n s i g n i f i c a n t d i f f e r e n c e s i n s k i n p e n e t r a t i o n o f h e x a c h l o r o b i p h e n y l between young and a d u l t r a t s , w h i l e i n v i v o r e s u l t s showed s i g n i f i c a n t d i f f e r e n c e s i n s k i n p e n e t r a t i o n between young and a d u l t r a t s a t a l l t i m e p o i n t s . Methods c o m p a r i s o n o f s k i n p e n e t r a t i o n o f c h l o r d e c o n e (Kepone) i s shown i n T a b l e V I . I n v i t r o s k i n a b s o r p t i o n v a l u e s o f c h l o r d e c o n e i n young and a d u l t r a t s were s i g n i f i c a n t l y lower t h a n i n v i v o v a l u e s . S k i n a b s o r p t i o n v a l u e s i n young a t 6 h were 0.45, 0.022, and 0.51% as d e t e r m i n e d by f l o w , s t a t i c , and i n v i v o methods, r e s p e c t i v e l y . I n a d u l t s , s k i n a b s o r p t i o n v a l u e s a t 6 h were 0.052, 0.026, and 0.398% as d e t e r m i n e d by f l o w , s t a t i c , and i n v i v o methods, r e s p e c t i v e l y . S k i n a b s o r p t i o n v a l u e s i n young a t 72 h were 1.4, 2.2, and 9.1% as d e t e r m i n e d by f l o w , s t a t i c and i n v i v o methods, r e s p e c t i v e l y . I n a d u l t s , 72 h s k i n a b s o r p t i o n v a l u e s were 1.2, 2.2, and 7.9% as d e t e r m i n e d by f l o w , s t a t i c , and i n v i v o methods, r e s p e c t i v e l y . A l l t h r e e methods showed h i g h e r s k i n p e n e t r a t i o n o f c h l o r d e c o n e i n young compared t o a d u l t animals. PHYSIOLOGICAL MODELING A p h y s i o l o g i c a l compartmental model f o r c a r b o f u r a n dermal a b s o r p t i o n and d i s p o s i t i o n i s shown i n F i g u r e 1. The compartmental volumes ( V ) were t h e average w e i g h t o f k i d n e y , l i v e r , and body f o u n d i n t h e p r e s e n t s t u d y . The o t h e r compartmental volumes were d e r i v e d from t h e body p r o p o r t i o n s g i v e n by L u t z e t a l . ( 14)• C a r d i a c o u t p u t and b l o o d f l o w r a t e s were s c a l e d d i r e c t l y w i t h compartmental s i z e from t h e v a l u e s g i v e n by Bungay e t a l . ( 1 1 ) . A b l o o d f l o w r a t e f o r a 1.9 g k i d n e y was c a l c u l a t e d t o be 8.33 mL/min from a plasma f l o w r a t e o f 5 mL/min and h e m a t o c r i t o f 40% ( 1 5 ) . The system o f d i f f e r e n t i a l e q u a t i o n s d e s c r i b i n g t h e t r a n s f e r of m a t e r i a l between organ compartments i s g i v e n below. F o r b l o o d T
d i=K,L M,S
V. R.
For muscle and n o n t r e a t e d dt
y l
V
Y
B
Y
B " V.R. i i i
skin where
i = M,S.
Wang et al.; Biological Monitoring for Pesticide Exposure ACS Symposium Series; American Chemical Society: Washington, DC, 1988.
Wang et al.; Biological Monitoring for Pesticide Exposure ACS Symposium Series; American Chemical Society: Washington, DC, 1988. *
Age X t i m e
1.15±0.21
0.592±0.138
0.188±0.054
0.019±0.005
Adult
2.20
2.18
2.11
2.43
3.63
* *
33.2±2.2
28.1±3.5
13.62±0.53
2.50±0.20
Young/ a d u l t Young
* S i g n i f i c a n t a t p < 0.05 f o r t h e h y p o t h e s i s o f no y o u n g - a d u l t d i f f e r e n c e . NS Not s i g n i f i c a n t , p > 0.05.
NS
1.36±0.16 2.50±0.32
1.25±0.24
1.05
0.58±0.08 0.92
0.4610.12
1.00
Age
1.25±0.23
72
0.071±0.022
0.83
0.015±0.002
0.96
0.60±0.13
48
Young/ a d u l t Young
0.17±0.03
Penetration
S t a t i c System
% Skin
Adult
All
0.1710.04
0.012±0.003
Young
24
6
Time (h)
1
19.611.5
18.4±0.6
8.3510.53
0.63±0.06
Adult
In v i v o
*
*
1.65*
1.69*
1.53*
1.63*
3.94*
Young adult
Methods Comparison o f S k i n P e n e t r a t i o n o f 2 , 2 , 4 , 4 * , 5 , 5 ' - H e x a c h l o r o b i p h e n y l
Flow System
T a b l e V.
o
B W W
H Q
s
o
2
1
r 3 0
o
s
3
s
00
Wang et al.; Biological Monitoring for Pesticide Exposure ACS Symposium Series; American Chemical Society: Washington, DC, 1988.
0.921±0.052
1.201±0.057
1.398±0.057
24
48
72
1.234±0. 310
0.699±0. 243
0.205±0. 090
0.052±0. 020
1.84*
1.13*
1.80*
4.49*
8.69*
Young Adult
2.213±0.435
1.100±0.238
2.47±0.072
0.022±0.007
1.09
1.03
1.21
1.24
0.86
Young Adult
difference.
2.153±0.320
0.912±0.161
0.199±0.039
0.026±0.007
S t a t i c System Young Adult
% Skin Penetration
9.066±0.664
6.825±0.219
3.570*0.453
0.513*0.063
7.922±1.061
5.626±0.686
2.508±0.606
3.98±0.108
In V i v o Method Young Adult
Methods Comparison o f S k i n P e n e t r a t i o n o f C h l o r d e c o n e
* S i g n i f i c a n t a t p < 0.05 f o r t h e h y p o t h e s i s o f no y o u n g - a d u l t
All
0.450±0.043
Flow System Young Adult
6
Time (h)
Table V I .
1.21
1.14
1.21
1.42
1.29
Young Adult
180
BIOLOGICAL MONITORING FOR PESTICIDE EXPOSURE
Treated Skin
V
Blood
v
Liver
Feces
Kidney Urine
Skin
Muscle and Fat Figure 1. Physiological model for carbofuran dermal absorption and disposition in the rat. (Reproduced with permission from ref. 9. Copyright 1987 Hemisphere Publishing Corporation.)
Wang et al.; Biological Monitoring for Pesticide Exposure ACS Symposium Series; American Chemical Society: Washington, DC, 1988.
14. For
181
Absorption and Pharmacokinetics
S H A H E T A L .
kidney _d_ dt K Y
and f o r
VK
=
liver Y
Y
dt L
k
Y
V^ B " V R L B L L For t r e a t e d s k i n y
dt T
y
T
=
Y (0)
" V i '
T
Nomenclature
v
Dermal dose (n moles) R a d i o a c t i v i t y i n compartment i (n moles) B l o o d f l o w r a t e t o t i s s u e i : (mL/h) Volume f o r t i s s u e compartment i : (mL) Equilibrum tissue/blood r a t i o for compartment i Dermal a b s o r p t i o n r a t e c o n s t a n t ( h ~ ) Urinary e x c r e t i o n r a t e constant (h~ ) F e c a l e x c r e t i o n r a t e c o n s t a n t (h"^)
i R-
k k k
Subscripts B K L M S
1
A
T F U
1
y
F
Blood Kidneys Liver Muscle Nontreated skin Treated s k i n Feces Urine
C a r b o f u r a n l e v e l s from b l o o d , k i d n e y , l i v e r , s k i n , c a r c a s s , u r i n e , and f e c e s were f i t t e d t o the model u s i n g SAAM27 t o o p t i m i z e t h e parameters f o r e q u i l i b r u m t i s s u e / b l o o d r a t i o (R,p), t h e u r i n e ( K y ) , and f e c e s ( K ) , e x c r e t i o n - r a t e c o n s t a n t , and t h e d e r m a l a b s o r p t i o n - r a t e c o n s t a n t ( K ) . The parameter v a l u e s a r e shown i n Table V I I . The dermal a b s o r p t i o n - r a t e c o n s t a n t ( K ) f o r young, 0.0 0548 F
A
A
1
1
h " , i s about 3 t i m e s t h a t f o r a d u l t s , 0.00173 h " . The model r e s u l t s f o r dermal a b s o r p t i o n were i n agreement w i t h t h e o b s e r v e d v a l u e s a f t e r 24 h f o r b o t h young and a d u l t r a t s . B e f o r e 24 h, t h e model r e s u l t s were a p p r o x i m a t e l y h a l f o f t h e o b s e r v e d v a l u e s , perhaps i n d i c a t i n g an a d d i t i o n a l r a p i d component o f a b s o r p t i o n w h i c h was not i n c o r p o r a t e d i n t h e model. The u r i n a r y e x c r e t i o n r a t e c o n s t a n t s ( K ) were f o u n d t o be 36.1 h ~ f o r young and 26.1 h " f o r t h e a d u l t . The f e c a l e x c r e t i o n r a t e c o n s t a n t s ( K ) were found t o be 0.67 h ~ f o r young and 0.24 h ~ f o r the a d u l t . The i n c r e a s e d dermal a b s o r p t i o n - r a t e c o n s t a n t i n young compared t o a d u l t a n i m a l s appears t o be b a l a n c e d by the i n c r e a s e d e x c r e t i o n r a t e i n t h e young, such t h a t t h e body burdens i n young and a d u l t s a r e about t h e same a t 120 h. The e q u i l i b r i u m t i s s u e - t o - b l o o d r a t i o s ( T a b l e V I I ) f o r a d u l t a n i m a l s were h i g h e r t h a n t h o s e o f t h e r e s p e c t i v e organs i n t h e young. Most n o t a b l e i s t h e d i f f e r e n c e i n t h e k i d n e y - t o - b l o o d r a t i o of 10.3 f o r a d u l t s as compared t o 5.4 f o r young, i n d i c a t i n g the greater sequestering of carbofuran-derived r a d i o a c t i v i t y i n a d u l t s t h a n i n young. 1
y
1
p
1
1
Wang et al.; Biological Monitoring for Pesticide Exposure ACS Symposium Series; American Chemical Society: Washington, DC, 1988.
Wang et al.; Biological Monitoring for Pesticide Exposure ACS Symposium Series; American Chemical Society: Washington, DC, 1988.
_
t
F
b
b
c
b
b
1
1
6.38 ( 9 ) b 0.72 3.03 11.35 (16) 40.44 (57) 70.94° Kp = 0.674 h ~
K
b
14.18 ( 9 ) 1.31 5.93 25.21 (16) 89.82 (57) 154.58 = 0.239 h "
±
V (mL) Q ±
(mL/min)
K
K
A
A = 0.00548 h "
17.74 3.195.41 4.861.91 1.421.28 2.242.38
A = 0.00173 h "
39.4010.29 5.782.47 9.491.94 3.153.65 4.98
1
1
P a r a m e t e r s Employed i n t h e P h y s i o l o g i c Model f o r C a r b o f u r a n A b s o r p t i o n and D i s p o s i t i o n i n t h e Young and A d u l t R a t *
from J . T o x i c o l . Environ.
Health.
Observed.
c
* Reprinted
P e r c e n t o f body w e i g h t g i v e n i n p a r e n t h e s e s .
b
22:207-223, 1987 w i t h p e r m i s s i o n o f p u b l i s h e r .
V^, compartmental volume; Q^ b l o o d f l o w r a t e t o t h e o r g a n s ; R^, e q u i l i b r i u m t i s s u e t o b l o o d r a t i o ; Ky, r a t e c o n s t a n t f o r u r i n a r y e x c r e t i o n ; Kp, r a t e c o n s t a n t f o r f e c a l e x c r e t i o n ; K , r a t e c o n s t a n t f o r dermal a b s o r p t i o n .
a
1
Blood Kidneys Liver Skin M u s c l e and f a t Body Ky = 36.06h"
Young
1
Blood Kidneys Liver Skin M u s c l e and f a t Body ky = 26.09 h "
Organ
Adult
Rat
TABLE V I I .
r—
GO
o
w W
3
H
3
O
2
O
o
P
5
8
gg
14.
183
Absorption and Pharmacokinetics
SHAH ET AL.
A s t e a d y s t a t e was r e a c h e d r a p i d l y . The model p r e d i c t e d o r g a n c o n t e n t t o be maximum a t 6 h, f o l l o w e d by a d e c r e a s e i n c o n t e n t as a r e s u l t o f t h e d e c l i n e i n t h e amount t h a t was a v a i l a b l e f o r p e n e t r a t i o n . C o n t i n u o u s e x p o s u r e was s i m u l a t e d w i t h t h e model by m a i n t a i n i n g a u n i t c o n s t a n t amount on t h e s k i n . E q u i l i b r i u m l e v e l s c a l c u l a t e d i n t h e o r g a n s as f r a c t i o n s o f t h e amount on t h e s k i n f o r young and a d u l t , r e s p e c t i v e l y , were 1.5 X 4
10" ,
and
liver, 10~
4
9.4
0.65
X 10~
X 10"
4
4
and
f o r kidney, 4.7
f o r t h e t o t a l body.
h) f o r young and 4
X
10~
4
X 10""
and
f o r s k i n , and
Corresponding
a d u l t s were 52 X 1
4
3.7
10" 4
4
1.4
X 10~
81 X 1 0 ~
4
excretion rates and
17 X 1 0 ~
4
h"
4
and
for 40
X
(fraction/ 1
for urine
1
and 2.5 X 1 0 ~ h " and 0.34 X 1 0 ~ h " f o r f e c e s . From t h i s t e m p o r a l e x p e r i m e n t w i t h a s i n g l e a p p l i e d dose o f c a r b o f u r a n , t h e l i n e a r compartmental f l o w model p r o v i d e s a good f i t t o t h e d a t a . A more complete v a l i d a t i o n o f t h e model would r e q u i r e d a t a a t a sequence o f doses as w e l l as d a t a from m u l t i p l e dose e x p e r i m e n t s . F o r c h l o r d e c o n e , a model d e v e l o p e d from i n t r a v e n o u s ( i v ) d o s i n g was used b u t m o d i f i e d t o accommodate t h e dermal a b s o r p t i o n pathway. A t i m e - v a r y i n g dermal a b s o r p t i o n r a t e c o n s t a n t was f o u n d t o enhance t h e model f i t . The u r i n a r y e x c r e t i o n r a t e c o n s t a n t was a l s o time-dependent. E x c r e t i o n began a t about 0.75 h"^ and f i n i s h e d a t about 0.01 a t 120 h. Equilibrium tissue/blood r a t i o s a g r e e d w i t h t h o s e f o u n d by i v d o s i n g e x c e p t f o r s k i n . Skin was f o u n d t o have an e q u i l i b r i u m t i s s u e / b l o o d r a t i o o f about 3.5 i n s t e a d o f 6 as d e t e r m i n e d by i v d o s i n g . T h i s was t h e l o w e s t r a t i o f o r any t i s s u e . The h i g h e s t r a t i o was 10 w h i c h o c c u r r e d f o r liver. Dermal a b s o r p t i o n f o r d i n o s e b was b i p h a s i c r e q u i r i n g two f i r s t o r d e r compartments t o a d e q u a t e l y s i m u l a t e t h e o b s e r v e d data. T i s s u e / b l o o d r a t i o s were l o w e s t i n muscle, about 0.15, and h i g h e s t i n k i d n e y , about 0.55. S i n c e a l l r a t i o s were l e s s t h a n 1.0, no s e q u e s t e r i n g o f d i n o s e b r a d i o a c t i v i t y i s i n d i c a t e d . The u r i n a r y pathway was t h e p r e f e r r e d r o u t e o f e x c r e t i o n by about a 4:1 r a t i o as compared t o t h e f e c a l r o u t e . H e x a c h l o r o b i p h e n y l was modeled w i t h s e p a r a t e compartments f o r p a r e n t and m e t a b o l i t e as d e t e r m i n e d from p u b l i s h e d i v e x p e r i m e n t s (14). Dermal a b s o r p t i o n was d e s c r i b e d by a s i n g l e f i r s t o r d e r compartment b u t d e l a y e d by a b o u t 1 h i n young r a t s and 4 h i n adult rats. The t i s s u e / b l o o d r a t i o f o r a d i p o s e f o r t h e p a r e n t compound was f o u n d t o be i n t h e 100's o r 1000's i n d i c a t i n g a v e r y s m a l l r e l e a s e o f p a r e n t from t h e a d i p o s e compartment. M u s c l e had t h e l o w e s t t i s s u e / b l o o d r a t i o f o r p a r e n t o f about 4. The m e t a b o l i s m c o n s t a n t f o r l i v e r was about 0.02 mL/min which i s q u i t e slow. The m e t a b o l i t e s a r e r e a d i l y e x c r e t e d and p r o d u c e d t i s s u e b l o o d r a t i o s o f o n l y 1 t o 4. DISCUSSION: A number o f s t u d i e s have s u g g e s t e d h i g h e r s k i n p e r m e a b i l i t y i n premature and f u l l - t e r m i n f a n t s compared t o a d u l t s . B e h l e t a l . (4) and Maibach and B o i s i t s (16) have r e v i e w e d t h e l i t e r a t u r e on
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a g e - r e l a t e d p e r c u t a n e o u s a b s o r p t i o n . B e h l e t a l . (4,17) r e p o r t e d i n v i t r o s k i n p e n e t r a t i o n o f w a t e r , methanol, e t h a n o l , b u t a n o l , h e x a n o l , and o c t a n o l i n male h a i r l e s s mice o f d i f f e r e n t ages. They o b s e r v e d i n c r e a s e d s k i n p e r m e a b i l i t i e s r e a c h i n g maximum v a l u e s around 25 days o f age, t h e n d e c l i n i n g s h a r p l y up t o about 60 days o f age, and r e m a i n i n g more o r l e s s i n v a r i a n t t h e r e a f t e r . In t h e p r e s e n t s t u d y , a g e - r e l a t e d d i f f e r e n c e s i n p e r c u t a n e o u s a b s o r p t i o n o f some o f t h e p e s t i c i d e s t e s t e d were o b s e r v e d . I n many c a s e s s i g n i f i c a n t i n f l u e n c e o f methods employed t o d e t e r m i n e t h e s k i n a b s o r p t i o n o f t h e s e p e s t i c i d e s was a l s o o b s e r v e d . R e s u l t s a t 72 h f r o m t h e i n v i v o method showed a g e - r e l a t e d d i f f e r e n c e s i n s k i n p e n e t r a t i o n f o r c a r b o f u r a n , d i n o s e b , and hexachlorobiphenyl. The f l o w method showed s t a t i s t i c a l l y s i g n i f i c a n t s k i n p e n e t r a t i o n d i f f e r e n c e s f o r dinoseb, c a r b a r y l , c a r b o f u r a n and h e x a c h l o r o b i p h e n y l . The s t a t i c method showed s i g n i f i c a n t young/adult p e n e t r a t i o n d i f f e r e n c e s only f o r c a r b o f u r a n and h e x a c h l o r o b i p h e n y l . T h i s study c l e a r l y demonstrates t h a t s i g n i f i c a n t d i f f e r e n c e s i n a b s o l u t e p e n e t r a t i o n v a l u e s a r i s e from t h e d i f f e r e n t methods used. A number o f s t u d i e s have shown good c o r r e l a t i o n between i n v i v o and i n v i t r o s k i n p e r m e a b i l i t y v a l u e s f o r a number o f c h e m i c a l s and a n i m a l s p e c i e s because s k i n a b s o r p t i o n has been c o n s i d e r e d as t h e p a s s i v e d i f f u s i o n p r o c e s s t h r o u g h a r a t e l i m i t i n g , n o n l i v i n g b a r r i e r , s t r a t u m corneum. F r a n z (18) compared t h e p e r c u t a n e o u s a b s o r p t i o n ( i n v i t r o ) o f 12 o r g a n i c compounds w i t h i n v i v o r e s u l t s r e p o r t e d by Feldmann and Maibach ( 1 9 ) . He r e p o r t e d e x c e l l e n t q u a l i t a t i v e agreement between i n v i t r o and i n v i v o methods. He f u r t h e r r e p o r t e d t h e d i s c r e p a n c i e s i n t h e q u a n t i t a t i v e agreement between t h e two s e t s o f d a t a . L a t e r on F r a n z (20) r e p o r t e d t h a t d i s c r e p a n c i e s i n q u a n t i t a t i v e agreement was due s i m p l y t o e x p e r i m e n t a l v a r i a t i o n based on a d d i t i o n a l i n v i t r o e x p e r i m e n t s t o s i m u l a t e i n v i v o c o n d i t i o n s by w a s h i n g s k i n a f t e r 24 h. Bronaugh (21) r e p o r t e d i d e n t i c a l i n v i v o and i n v i t r o rat s k i n absorption values f o r benzoic a c i d , a c e t y l s a l i c y l i c a c i d and u r e a . The two i n v i t r o methods u t i l i z e d h e r e , namely, t h e s t a t i c and f l o w - t h r o u g h d i f f u s i o n c e l l s , have been r e c e n t l y compared by Bronaugh and S t e w a r t ( 2 2 ) . The a u t h o r s (22) r e p o r t e d t h e c o m p a r a t i v e s k i n a b s o r p t i o n v a l u e s f o r w a t e r , c o r t i s o n e , and b e n z o i c a c i d t h r o u g h r a t s k i n as d e t e r m i n e d by s t a t i c and f l o w through d i f f u s i o n c e l l s . They r e p o r t e d s i m i l a r a b s o r p t i o n p r o f i l e s and q u a n t i t a t i v e v a l u e s between t h e two d i f f u s i o n systems f o r w a t e r , c o r t i s o n e , and b e n z o i c a c i d under t h e e x p e r i m e n t a l conditions described. However, d i s c r e p a n c i e s i n a b s o r p t i o n v a l u e s were o b s e r v e d f o r a h y d r o p h o b i c compound, [3-phenyl-2-propenyl-2aminobenzoate ( c i n n a m y l a n t h r a n i l a t e ) ] between t h e two d i f f u s i o n c e l l systems; t h e f l o w - t h r o u g h d i f f u s i o n c e l l system gave enhanced a b s o r p t i o n v a l u e f o r c i n n a m y l a n t h r a n i l a t e compared t o t h e s t a t i c c e l l system. They have f u r t h e r r e p o r t e d good agreement between i n v i v o and i n v i t r o ( s t a t i c as w e l l as f l o w - t h r o u g h d i f f u s i o n c e l l s ) s k i n p e r m e a t i o n f o r c o r t i s o n e and b e n z o i c a c i d when each was applied i n petrolatum v e h i c l e . We have r e p o r t e d d i s c r e p a n c i e s i n t h e s k i n a b s o r p t i o n v a l u e s as d e t e r m i n e d by t h e two i n v i t r o methods. We a l s o o b s e r v e d p o o r
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c o r r e l a t i o n between i n v i v o and i n v i t r o r e s u l t s f o r t h e s e h i g h l y complex p e s t i c i d a l c h e m i c a l s . There a r e a number o f f a c t o r s t h a t can i n f l u e n c e t h e s k i n a b s o r p t i o n measurements. The i n f l u e n c e o f r e c e p t o r f l u i d f o r i n v i t r o s k i n a b s o r p t i o n measurements has been w i d e l y documented. F o r example, t h e i n v i t r o a b s o r p t i o n o f c h l o r d e c o n e and h e x a c h l o r o b i p h e n y l i n t h e p r e s e n t s t u d y n e v e r exceeded more t h a n t h a n 2.5% i n b o t h d i f f u s i o n c e l l systems. These two c h e m i c a l s have p o o r w a t e r s o l u b i l i t y (0.9 ppb f o r h e x a c h l o r o b i p h e n y l ) and t h e r e c e p t o r f l u i d u t i l i z e d i n t h i s i n v e s t i g a t i o n may n o t be s u f f i c i e n t l y l i p o h i l i c t o remove t h e c h e m i c a l from t h e d e r m i s ( s p l i t - t h i c k n e s s s k i n ) . Bronaugh and S t e w a r t (23) s u g g e s t e d t h a t t h e l a c k o f s o l u b i l i t y o f t h e h y d r o p h o b i c p e n e t r a n t i n t o t h e r e c e p t o r f l u i d f o r i n v i t r o methods c o u l d be a c o n t r i b u t i n g f a c t o r a c c o u n t i n g f o r i n v i v o and i n v i t r o d i s c r e p a n c i e s i n s k i n a b s o r p t i o n v a l u e s . Bronaugh and S t e w a r t (23) r e p o r t e d maximum a b s o r p t i o n o f c i n n a m y l a n t h r a n i l a t e by u s i n g 6% PEG-20 o l e y l e t h e r r e c e p t o r f l u i d w i t h e i t h e r t y p e o f d i f f u s i o n c e l l system. R e c e n t l y , S c o t t and Ramsey (24) r e p o r t e d t h a t t h e h i g h e s t a b s o r p t i o n o f c y p e r m e t h r i n was a c h i e v e d when 50% aqueous e t h a n o l was used as t h e r e c e p t o r f l u i d w h i c h was i n agreement w i t h i n v i v o a b s o r p t i o n t h r o u g h t h e r a t s k i n . They f u r t h e r r e p o r t e d t h a t t h e a b s o r p t i o n o f c y p e r m e t h r i n measured w i t h two o t h e r r e c e p t o r f l u i d s (6% V o l p o 20 and 20% f e t a l c a l f serum) was v e r y s i m i l a r t o 50% aqueous e t h a n o l as t h e r e c e p t o r f l u i d . Thus t h e above mentioned study suggests t h a t , the s o l u b i l i t y of the penetrant i n t o r e c e p t o r f l u i d , r a t h e r than the d i f f u s i o n of penetrant through the e p i d e r m a l membrane, i s t h e r a t e l i m i t i n g s t e p . I t appears t h a t t h e r e s u l t s o b t a i n e d by d i f f e r e n t methods have t o be c a r e f u l l y e v a l u a t e d w i t h t h e e x p e r i m e n t a l c o n d i t i o n s prescribed. I t i s a l s o c l e a r from t h e l i t e r a t u r e t h a t t h e i n v i t r o r e s u l t s can be i n f l u e n c e d by a number o f f a c t o r s . Perhaps more c o m p a r a t i v e s t u d i e s may improve t h e u n d e r s t a n d i n g o f t h e i n v i t r o and i n v i v o c o r r e l a t i o n . V a l i d a t i o n o f r e c e n t l y recommended g u i d e l i n e s f o r i n v i t r o p e r c u t a n e o u s p e n e t r a t i o n s t u d i e s (25) w i t h a number o f c h e m i c a l s may h e l p i n u n d e r s t a n d i n g t h e i n v i t r o s k i n absorption process. U t i l i t y o f p h a r m a c o k i n e t i c models has been e x p l o r e d f o r e x t r a p o l a t i o n t o man, a n i m a l s p e c i e s s c a l i n g , e x t r a p o l a t i o n o f r e s u l t s beyond t h e o b s e r v e d t i m e p o i n t , s i m u l a t i o n o f c o n t i n u o u s or m u l t i p l e exposure s i t u a t i o n , t i s s u e dose e x t r a p o l a t i o n , i m p r o v i n g e x p e r i m e n t a l d e s i g n , and o v e r a l l r e d u c t i o n o f a n i m a l usage. P h y s i o l o g i c a l models have been shown t o be adequate f o r o t h e r c h e m i c a l s (26,27). The a p p l i c a t i o n s o f p h y s i o l o g i c a l l y based m o d e l i n g and i t s t e c h n i q u e has been r e v i e w e d by a number o f i n v e s t i g a t o r s (26,28,29). I n t h e p r e s e n t s t u d y , p h y s i o l o g i c a l l y based p h a r m a c o k i n e t i c models were used t o d e c r i b e dermal a b s o r p t i o n and d i s p o s i t i o n p r o c e s s e s f o r t h e c h e m i c a l s s t u d i e d . Rate c o n s t a n t s f o r dermal a b s o r p t i o n , and u r i n a r y and f e c a l e x c r e t i o n , as w e l l as t i s s u e t o b l o o d steady s t a t e r a t i o s were determined. A p h y s i o l o g i c a l model d e s c r i b i n g c a r b a r y l r a d i o a c t i v i t y was f i t t e d t o t h e t i s s u e d i s t r i b u t i o n d a t a . The dermal a b s o r p t i o n was f o u n d t o be d e s c r i b e d by a s i n g l e f i r s t o r d e r compartment f o r b o t h
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young and a d u l t r a t s o v e r t h e e x p e r i m e n t a l p e r i o d . The o r d e r o f t h e e q u i l i b r i u m t i s s u e / b l o o d r a t i o s was t h e same i n young and a d u l t r a t s . The t i s s u e w i t h t h e l a r g e s t t i s s u e / b l o o d r a t i o o f about 6 o r 7 was k i d n e y . The u n t r e a t e d s k i n has t h e l o w e s t e q u i l i b r i u m t i s s u e / b l o o d r a t i o o f about 0.8 t o 1.0. The r a t e c o n s t a n t f o r k i d n e y t o u r i n e e x c r e t i o n was l a r g e a t 15 t o 20 h"^. A more complex model t o i n c l u d e m e t a b o l i s m , b l o o d c l e a r a n c e , r e l e a s e o f chemical from s o l v e n t t o s k i n , i n c o r p o r a t i o n o f v i a b l e l a y e r , and m e t a b o l i s m d u r i n g a b s o r p t i o n , e t c . , may a i d i n i m p r o v i n g t h e model's u t i l i t y . CONCLUSIONS; P e r c u t a n e o u s a b s o r p t i o n was compared i n young and a d u l t F i s h e r 344 r a t s f o r f i v e p e s t i c i d e s u t i l i z i n g b o t h i n v i v o and i n v i t r o methods. I n v i v o p e n e t r a t i o n o f t h e p e s t i c i d e s d u r i n g a 72 h p e r i o d , ranged from a p p r o x i m a t e l y 8.0% ( c h l o r d e c o n e , a d u l t ) t o 84% ( d i n o s e b , a d u l t ) , d e p e n d i n g on compound and age o f t h e a n i m a l . Three p e s t i c i d e s , ( c a r b o f u r a n , h e x a c h l o r o b i p h e n y l , and c h l o r d e c o n e ) showed h i g h e r s k i n p e n e t r a t i o n v a l u e s i n young compared t o a d u l t . D i f f e r e n c e s i n s k i n p e n e t r a t i o n v a l u e s were o b s e r v e d among p e s t i c i d e s due t o methods o f measurement. Two i n v i t r o methods, namely, s t a t i c c e l l and f l o w - t h r o u g h d i f f u s i o n c e l l systems gave d i f f e r e n t p e n e t r a t i o n v a l u e s . A p h y s i o l o g i c a l compartmental model a p p e a r s t o be good f o r s i m u l a t i n g dermal a b s o r p t i o n and d i s p o s i t i o n o f t h e p e s t i c i d e s s t u d i e d . ACKNOWLEDGMENTS: T h i s work was c o n d u c t e d a t N o r t h r o p E n v i r o n m e n t a l Sciences, Research T r i a n g l e P a r k , NC. The r e s e a r c h d e s c r i b e d i n t h i s a r t i c l e has been r e v i e w e d by t h e O f f i c e o f T o x i c S u b s t a n c e s , U.S. E n v i r o n m e n t a l P r o t e c t i o n Agency, and approved f o r p u b l i c a t i o n . A p p r o v a l does n o t s i g n i f y t h a t t h e c o n t e n t s n e c e s s a r i l y r e f l e c t t h e v i e w s and p o l i c i e s o f t h e Agency, n o r does mention o f t r a d e names o r c o m m e r c i a l p r o d u c t s c o n s t i t u t e endorsement o r recommendation f o r u s e .
Literature Cited 1. 2. 3. 4.
5. 6. 7.
Synthetic Organic Chemicals , United States International Trade Commission, 1985, pp 226-241. Durham, W.F.; Wolfe, H.R. Bull. WHO 1962, 26 , 75-91. Wolfe, H.R.; Durham, W.F.; Armstrong, J.F.Arch.Environ. Health 1976, 14 , 622-633. Behl, C.R.; Bellantone, N.H.; Flynn, G.L. In Percutaneous Absorption Mechanisms - Methodology - Drug Delivery . Bronaugh, R.L., Maibach, H.I.; Eds.; Dekker: New York, 1985; pp 183-212. Nachman, R.L.; Esterly, N.B.J. Pediatr . 1971, 79 , 628-632. Wester, R.C.; Noonan, P.K.; Cole, M.P.; Maibach, H.I. Pediatr. Res . 1977, 11 , 737-739. Knaak, J.B.; Yee, K., Ackerman, CR., Zweig, G., Wilson, B.W. Toxicol. Appl. Pharmacol . 1984, 72 , 406-416.
Wang et al.; Biological Monitoring for Pesticide Exposure ACS Symposium Series; American Chemical Society: Washington, DC, 1988.
14. SHAHETAL.
Absorption and Pharmacokinetics
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8. Shah, P.V.; Fisher, H.L.; Sumler, M.R; Chernoff, N.; Hall, L.L. J. Toxicol. Environ. Health 1987, 21 , 353-366. 9. Shah, P.V.; Fisher, H.L.; Month, N.J.; Sumler, M.R.; Hall, L.L. J. Toxicol. Environ. Health 1987, 22 ; 207-223. 10. SAS Institute Inc. SAS User's Guide: Statistics Version-5 Edition, SAS Institute, Inc., Cary, NC 1985. 11. Bungay, P.M.; Dedrick, R.L.; Matthews, H.B.Ann. N.Y. Acad. Sci . 1979, 320 , 257-270. 12. Bungay, P.M., Dedrick, R.L., Matthews, H.B. J. Pharmacokinet. Biopharm . 1981, 309-341. 13. Berman, M., Weiss, M.F. SAAM Manual. (Simulation, Analysis and Modeling) , Version: SAAM 27. Department of Health, Education, and Welfare, Publication (NIH) 78-180, 1978. 14. Lutz, R.J.; Dedrick, R.L.; Matthews, H.B.; Eling, T.E; Anderson, M.W. Drug. Metab. Dispos . 1977, 54 , 386-397. 15. Bischoff, K.B., Dedrick, R.L.; Zaharko, D.S.; Longstreth, J.A.J. Pharm. Sci . 1971, 60 , 1129-1133. 16. Maibach, H.I.; Boisits, E.K. Neonatal Skin Structure and Function ; Dekker: New York, 1982. 17. Behl, C.R.; Flynn, G.L.; Kurihara, T.; Smith, W.M.; Bellantone, N.H., Gatmaitan, O.; Pierson, C.L.; Higuchi, W.I.; HO, N.F.H. J. Soc. Cosmet. Chem. 1984, 35 , 237-252. 18. Franz, T.J. J. Invest. Dermatol . 1975, 64 , 190-195. 19. Feldmann, R.J.; Maibach, H.I. J. Invest. Dermatol . 1970, 54 , 399-404. 20. Franz, T.J. Curr. Probl. Dermatol . 1978, 7, 58-68. 21. Bronaugh, R.L.; Stewart, R.F.; Congdon, E.R. Toxicol. Appl. Pharmacol. 1982, 62 , 481-488. 22. Bronaugh, R.L.; Stewart, R.F.J. Pharm. Sci . 1985, 74 , 6467. 23. Bronaugh, R.L.; Stewart, R.F. J. Pharm. Sci. 1984,73, 12551257. 24. Scott, R.C.; Ramsey, J.D.J. Invest. Dermatol . 1987,89, 142146. 25. Skelly, J.P.; Shah, V.P.; Maibach, H.I.; Guy R.H.; Wester, R.C.; Flynn, G.; Yacobi, A. Pharm. Res . 1987, 4 , 265-267. 26. Anderson, M.E.; Keller, W.C. InCutaneous Toxicity. Target Organ Toxicology Series ; Drill, V.A.,; Lazar, P., Eds., Raven Press, New York, 1982. p 9-27. 27. McDougal, J.N.; Jepson, G.W.; Clewell III, H.J.; MacNaughton, M.G.; Anderson, M.E. Toxicol. Appl Pharmacol . 1986, 85 , 286-294. 28. Lutz, R.J.; Dedrick, R.L.; Zaharko, D.S. Pharmacol. Ther . 1980, 11, 559-592. 29. Gerlowski, L.E.; Jain, R.K.J. Pharm. Sci . 1983, 72 , 11031127. RECEIVED July 5,1988
Wang et al.; Biological Monitoring for Pesticide Exposure ACS Symposium Series; American Chemical Society: Washington, DC, 1988.