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The Toxicologist - Society of Toxicology

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1335 IN VITRO EVALUATION OF INHIBITION OF<br />

BUTYRYLCHOLINESTERASE AND NEUROPATHY<br />

TARGET ESTERASE CAUSED BY THE ENANTIOMERS<br />

OF METHAMIDOPHOS IN BLOOD OF HENS.<br />

G. L. Emerick 1, 2 , R. V. Oliveira 2 , K. A. Belaz 2 , M. Gonçalves 1 and G. H.<br />

DeOliveira 1 . 1 Department <strong>of</strong> Natural Active Principles and <strong>Toxicology</strong>, University<br />

Estadual Paulista, Araraquara, Sao Paulo, Brazil and 2 Department <strong>of</strong> Chemistry,<br />

Universidade Federal de São Carlos, Sao Carlos, Sao Paulo, Brazil.<br />

Compounds containing an asymmetric center can exist in two isomeric forms<br />

known as enantiomers. About 25% <strong>of</strong> pesticides in current use are chiral, and this<br />

percentage is still increasing as more pesticides with complex structures are introduced<br />

into application. <strong>The</strong>se enantiomers usually have the same physical and<br />

chemical properties, however, <strong>of</strong>ten different biological activity. Methamidophos,<br />

which has an asymmetric center at the phosphorus atom, is one <strong>of</strong> organophosphate<br />

pesticides in the broader spectrum <strong>of</strong> action and also the highest toxicity.<br />

Thus, the objective <strong>of</strong> this work was to evaluate the in vitro IC50 <strong>of</strong> is<strong>of</strong>orms <strong>of</strong><br />

methamidophos in relation to plasma cholinesterase (BChE) and neuropathy target<br />

esterase in lymphocytes (LNTE) <strong>of</strong> hens. For determination <strong>of</strong> BChE and LNTE<br />

activity was used the method <strong>of</strong> Ellman et al. (1961) and Schwab and Richardson<br />

(1986), respectively, supplemented with different concentrations <strong>of</strong> methamidophos<br />

in order to estimate the constant <strong>of</strong> enzyme inhibition and IC50. <strong>The</strong> form<br />

(+)-Methamidophos had lower IC50 for the BChE (2.2 ± 0.40 mM). <strong>The</strong> racemic<br />

form showed intermediate IC50 (4.3 ± 0.23) and Ki (2.4 mM-1). <strong>The</strong> (-)-<br />

Methamidophos had the highest IC50 (6.4 ± 0.30) and lowest Ki (1.6 mM-1),<br />

therefore, less toxicity in vitro for the BChE. Regarding LNTE activity, the inhibitory<br />

concentrations have shown that the form (+)-Methamidophos had lower<br />

IC50. <strong>The</strong> positive form <strong>of</strong> methamidophos showed an IC50 value <strong>of</strong> approximately<br />

6 times smaller than the negative form. <strong>The</strong>se results showed significant differences<br />

in toxicity among the three is<strong>of</strong>orms <strong>of</strong> methamidophos in relation to<br />

BChE and NTE and that it is necessary to undertake further studies in order to reduce<br />

the toxic effects on non target species. Animal Committee <strong>of</strong> Ethics,<br />

Resolution: 24/2009. Financial support: FAPESP, grant number 09/51048-8.<br />

1336 CLUSTERING OF SERINE HYDROLASES BY<br />

SIMILARITIES OF INHIBITION PATTERNS TOWARD<br />

THE 4 STEREOISOMERS OF ISOMALATHION AGREES<br />

WITH PHYLOGENETIC PROXIMITIES INFERRED<br />

FROM SEQUENCE ALIGNMENTS.<br />

S. J. Wijeyesakere 1 , S. Jianmongkol 1 , J. A. Doorn 1 , B. R. Marable 1 , C. M.<br />

Thompson 2 , I. I. Baskin 3 , V. A. Palyulin 3 , G. F. Makhaeva 4 and R. J.<br />

Richardson 1 . 1 <strong>Toxicology</strong> Program, Department <strong>of</strong> Environmental Health Sciences,<br />

University <strong>of</strong> Michigan, Ann Arbor, MI, 2 Department <strong>of</strong> Pharmaceutical Sciences,<br />

University <strong>of</strong> Montana, Missoula, MT, 3 Department <strong>of</strong> Chemistry, M.V. Lomonosov<br />

Moscow State University, Moscow, Russian Federation and 4 Institute <strong>of</strong> Physiologically<br />

Active Compounds, Russian Academy <strong>of</strong> Sciences, Chernogolovka, Russian Federation.<br />

<strong>The</strong> purpose <strong>of</strong> the present study was to test the hypothesis that the relative stereoselectivity<br />

<strong>of</strong> serine hydrolases toward inhibition by the 4 stereoisomers <strong>of</strong> isomalathion<br />

is reflected in the phylogenetic order inferred from the aligned sequences <strong>of</strong><br />

each hydrolase. Bimolecular rate constants <strong>of</strong> inhibition (ki) <strong>of</strong> each <strong>of</strong> the 4<br />

stereoisomers <strong>of</strong> isomalathion were determined for human (Hu), bovine (Bo), rat<br />

(Ra), chicken (Ck), electric eel (Ee), and Torpedo californica (Tc) acetylcholinesterase<br />

(AChE); equine (Eq) and Hu butyrylcholinesterase (BChE); and Bo<br />

cholesterol esterase (CholE). A scatterplot matrix (Systat 13.00.05) <strong>of</strong> normalized<br />

ki values showed that the order <strong>of</strong> similarity <strong>of</strong> serine hydrolases was HuAChE =<br />

BoAChE > RaAChE > CkAChE > EeAChE = TcAChE > EqBChE = HuBChE ><br />

BoCholE. Moreover, neighbor-joining cluster analysis (Statistica 9.1) <strong>of</strong> normalized<br />

ki values generated a dendrogram with the same ordering as that observed in the<br />

scatterplot matrix. Finally, these orderings were in accord with the phylogenetic<br />

order inferred from maximum likelihood sequence alignments (ClustalX2 and<br />

GeneDoc 2.4). <strong>The</strong> results suggest that isomalathion stereoisomers may be useful<br />

probes <strong>of</strong> active site topologies and phylogenetic relationships among diverse serine<br />

hydrolases. Supported in part by NIH T32 ES07062.<br />

1337 AGE-RELATED BEHAVIORAL EFFECTS OF<br />

METHOMYL IN BROWN NORWAY RATS.<br />

R. C. MacPhail, K. A. Jarema and P. M. Phillips. NHEERL, U.S. EPA, Research<br />

Triangle Park, NC.<br />

Methomyl is a cholinesterase-inhibiting carbamate pesticide that is used in the field<br />

on cotton and a variety <strong>of</strong> fruits and vegetables. Concerns have been raised generally<br />

about age-related differences in susceptibility to cholinesterase-inhibiting pesti-<br />

286 SOT 2011 ANNUAL MEETING<br />

cides, especially for children. This experiment, part <strong>of</strong> a larger program on life-stage<br />

susceptibility, compared methomyl effects on the behavior <strong>of</strong> adolescent, youngadult<br />

and middle-age male Brown Norway rats (Charles River, N=24/age) that were<br />

initially 1, 4 or 12 months <strong>of</strong> age, respectively. Another group <strong>of</strong> 12-month rats<br />

(NIA) was included to evaluate vendor differences. Testing occurred at weekly intervals<br />

in photocell devices that recorded horizontal and vertical locomotor activity<br />

during 30-min sessions. Methomyl (ChemService) was dissolved in deionized water<br />

and given orally in doses <strong>of</strong> 0 (i.e., vehicle), 0.5, 1.25, 2.0 and 2.75 mg/kg, 15-min<br />

before a test session. Order <strong>of</strong> dosing was counterbalanced so that each rat received<br />

all treatments. Following vehicle, horizontal activity was highest in young adults<br />

and roughly equal in adolescent and middle-age rats; vertical activity was highest in<br />

young adults, slightly lower in adolescents, and considerably lower in middle-age<br />

rats. Methomyl produced dose-related decreases in both horizontal and vertical activity.<br />

Adolescent rats were least affected. ED50s for horizontal activity were ca.<br />

5.72, 2.43 and 2.19 mg/kg for the adolescent, young-adult and middle-age rats, respectively.<br />

Corresponding ED50s for vertical activity were 4.41, 2.20 and 1.85<br />

mg/kg. Middle-age rats from NIA were similarly affected (horizontal ED50=1.96<br />

and vertical ED50=1.61 mg/kg). <strong>The</strong>se results indicate aging increases susceptibility<br />

to methomyl in Brown Norway rats; they also emphasize the importance <strong>of</strong> evaluating<br />

pesticide effects at multiple life stages in order to make informed inferences<br />

regarding susceptibility and risk. (This is an abstract <strong>of</strong> a proposed presentation and<br />

does not reflect US EPA policy.)<br />

1338 AGE-RELATED DIFFERENCES IN ACQUISTION,<br />

STEADY-STATE PERFORMANCE AND CARBARYL<br />

EFFECTS ON THE OPERANT BEHAVIOR OF BROWN<br />

NORWAY RATS.<br />

K. A. Jarema, P. M. Phillips and R. C. MacPhail. NHEERL, U.S. EPA, Research<br />

Triangle Park, NC.<br />

<strong>The</strong> rapid increase in older adults in the population highlights the importance <strong>of</strong><br />

understanding the role <strong>of</strong> aging in susceptibility to environmental contaminants.<br />

As part <strong>of</strong> a larger program on life-stage susceptibility, this experiment determined<br />

the effect <strong>of</strong> the carbamate pesticide carbaryl on the operant performance <strong>of</strong> youngadult,<br />

middle-age and senescent male Brown Norway rats. Rats (Charles River)<br />

were 4, 12, and 23-24 months old at the start <strong>of</strong> the experiment, weight-maintained,<br />

and trained to perform under a multiple variable-interval (VI) 10-sec variable-interval<br />

100-sec schedule <strong>of</strong> food reinforcement during 45-min test sessions.<br />

Once performances stabilized, one group (n=10-12/age) received each week a dose<br />

<strong>of</strong> carbaryl (3, 6.5 and 10 mg/kg) or corn oil, p.o., 30-minutes before testing. Doses<br />

were administered in a mixed order. A second group (n=11-12/age) received weekly<br />

carbaryl (10 mg/kg) and corn oil, p.o., at 30, 60, 120 or 240 minutes before testing;<br />

treatment times were also arranged in a mixed order. During acquisition, initial response<br />

rates for the senescent rats were lower than the young-adult rats, but increased<br />

to rates higher than young adults as performance stabilized. Acquisition for<br />

middle-age rats resembled young-adult rats early in training, and senescent rats late<br />

in training. Carbaryl produced dose-dependent decreases in responding, with the<br />

exception <strong>of</strong> 6.5 mg/kg in the middle-age rats. Senescent rats were overall most affected<br />

by carbaryl, especially under VI 100- sec following the lowest dose.<br />

Differences in performance due to age after the highest dose (10 mg/kg) were statistically<br />

insignificant. Senescent rats, however, took the longest to recover following<br />

10 mg/kg. Age-related differences in carbaryl effects demonstrate the importance<br />

<strong>of</strong> using a range <strong>of</strong> ages in order to make informed inferences about toxicant<br />

susceptibility and risk. (This is an abstract <strong>of</strong> a proposed presentation and does not<br />

reflect US EPA policy.)<br />

1339 CARBARYL NEUROTOXICITY ACROSS THE LIFE-SPAN<br />

OF THE BROWN-NORWAY RAT.<br />

V. C. Moser, P. M. Phillips and K. L. McDaniel. Toxicity Assessment Division, U.S.<br />

EPA, Research Triangle Park, NC.<br />

Demographics show that the proportion <strong>of</strong> older adults is increasing every year.<br />

While there has been considerable attention paid to potential sensitivity <strong>of</strong> the<br />

young to environmental chemicals, there is much less known about the relative vulnerability<br />

<strong>of</strong> the aged. Differences in response could be due to altered sensitivity as<br />

a result <strong>of</strong> toxicokinetic and/or toxicodynamic changes. We systematically compared<br />

the dose-response data across the age continuum for neurotoxicity produced<br />

by carbaryl, an N-methyl carbamate that produces acute toxicity via inhibition <strong>of</strong><br />

acetylcholinesterase (ChE). Male Brown-Norway rats were tested on postnatal day<br />

18 (PND18), and at 1, 4, 12, and 24 months <strong>of</strong> age (n=9-10/dose/age), and were<br />

orally gavaged with vehicle (corn oil), 3, 7.5, 15, or 22.5 mg/kg carbaryl.<br />

Horizontal (all ages) and vertical (rearing; adults only) motor activity was measured<br />

for 20 min beginning 15 min after dosing. Within 5 min after the activity session,<br />

rats were sacrificed and brain and RBC were collected for subsequent assay <strong>of</strong> ChE

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