27.07.2013 Views

The Toxicologist - Society of Toxicology

The Toxicologist - Society of Toxicology

The Toxicologist - Society of Toxicology

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

posure groups. However, the different exposure scenarios involving average styrene<br />

exposure or peak exposures did not significantly alter the performance to any test.<br />

Several factors could have influenced our results: definition <strong>of</strong> peaks, statistical<br />

power or short exposure time.<br />

1227 UTILITY OF C6-GLIOMA CELLS FOR EXPLORATORY<br />

RISK ASSESSMENT OF MIXTURES OF INSECTICIDES.<br />

D. M. Romero 1 , M. L. Kotler 1 and M. J. Wolansky 1, 2 . 1 Biological Chemistry<br />

(<strong>Toxicology</strong>), ARG NRC / University <strong>of</strong> Buenos Aires School <strong>of</strong> Science, Buenos Aires,<br />

Argentina and 2 ARG National Agency for Scientific and Technological Promotion,<br />

Buenos Aires, Argentina.<br />

Low levels <strong>of</strong> organophosphate (OP) and pyrethroid (PYR) insecticides may cooccur<br />

in real environments and food products. Considering each compound independently,<br />

these residue loadings may be considered safe for humans. However,<br />

there is a consensus on the need <strong>of</strong> considering joint neurotoxicity data to improve<br />

the accuracy <strong>of</strong> health risk estimates for these chemicals. We use a C6-glioma cell<br />

culture as an exploratory in vitro system derived from rat nervous system aimed to<br />

identify toxicologically relevant OP-PYR mixtures that may require cumulative risk<br />

analysis efforts in in vivo models. First, 4 OPs (chlorpyrifos; acephate; methidathion;<br />

diazinon) and 4 PYRs (type I: bifenthrin, tefluthrin; type II: α-cypermethrin,<br />

deltamethrin) were examined in single-compound assays carried out in C6cells<br />

after 4-48 hr exposure to each compound (0.1-250 μM). Threshold doses for<br />

cell viability status were determined using optical microscopy and MTT assays. We<br />

generated time- and dose-effect data, and ED15 values were computed from assays<br />

conducted at t=24 hr. In general, micromolar exposures produced dose-related alterations<br />

in cell viability at 24-48 hr. ED15s were 5-100 μM for PYRs and 5-30<br />

μM for OPs. Second, we evaluated the effects <strong>of</strong> each insecticide on nucleus morphology<br />

using Hoechst 33258 staining. We found dose-related increases in anomalous<br />

nuclei shapes from the low μM range up. Last, we examined a mixture <strong>of</strong> equitoxic<br />

levels <strong>of</strong> the 4 PYRs (1X mixture = Σ ED15) using the MTT assay. This<br />

type-I/II mixture produced a dose-related, dual joint action at 24 hr: while addition<br />

<strong>of</strong> individual effects was observed after exposure to the 1X mixture, dose-addition<br />

was apparent at a 0.1X dose, i.e., well below the single-compound thresholds for<br />

mitochondrial impact. We plan to evaluate other mixtures <strong>of</strong> insecticides in order<br />

to select toxicologically relevant combinations for in vivo testing <strong>of</strong> cumulative<br />

neurotoxicity.<br />

1228 BARIUM INTAKE IN THE CANARY ISLANDS: A TOTAL<br />

DIET STUDY.<br />

C. Rubio, D. González-Weller, J. Gutiérrez and A. Hardisson. <strong>Toxicology</strong>,<br />

University <strong>of</strong> La Laguna, La Laguna, Spain. Sponsor: A. Anadon.<br />

Barium (Ba) is a divalent metal widely distributed in nature. Commercial uses make<br />

it a potential food contaminant. <strong>The</strong> main sources <strong>of</strong> exposure for humans are food<br />

consumption, water consumption, and inhalation. Ba appears in many common<br />

foods at concentrations ranging from 0.21 to 11.0 mg/kg. Chronic exposure to this<br />

element is <strong>of</strong>ten associated with toxic effects on the cardiovascular system <strong>of</strong> mammals.<br />

Objectives: To quantify the concentration <strong>of</strong> Ba in 22 food groups as categorized<br />

by the Canary Islands Nutrition Survey (ENCA, 2000) and to estimate the<br />

total Ba intake in various segments <strong>of</strong> the population and the general population.<br />

Material and Methods: A total <strong>of</strong> 440 samples were analyzed to determine the Ba<br />

levels in various food groups. Ba was determined by Optical Emission Spectrometry<br />

with Inductively Coupled Plasma (ICP-OES). Results: <strong>The</strong> average concentration <strong>of</strong><br />

Ba in the analyzed food groups was 0.65 mg/kg, implying an intake <strong>of</strong> 0.69 mg/day<br />

<strong>of</strong> Ba in the adult population <strong>of</strong> the Canary Islands. All groups had detectable Ba levels.<br />

Concentration levels ranged from 0.04 ± 0,04 mg/L in water to 5.21 ± 2,12<br />

mg/kg in nuts. <strong>The</strong> food consumption patterns <strong>of</strong> various genders and age groups<br />

were considered along with the Ba levels in the 22 food groups. <strong>The</strong> highest estimated<br />

dietary intake levels were observed in the 45-54 age group, for both men and<br />

women. Conclusions: This study demonstrates the need to assess, understand and<br />

monitor both the levels <strong>of</strong> metals in various food groups and the dietary intake <strong>of</strong> the<br />

population, in order to determine a safe intake level.<br />

1229 HOUSE DUST-MEDIATED PAH EXPOSURES RELATED<br />

TO SEALED PARKING LOTS MAY EXCEED DIETARY<br />

INTAKES IN CHILDREN.<br />

E. S. Williams 1 , B. J. Mahler 2 and P. C. Van Metre 2 . 1 Center for Reservoir and<br />

Aquatic Systems Research, Baylor University, Waco, TX and 2 U.S. Geologic Survey,<br />

Austin, TX.<br />

Most assessments have indicated that dietary ingestion is the primary route <strong>of</strong> exposure<br />

to carcinogenic polycyclic aromatic hydrocarbons (B2 PAHs; the seven PAH<br />

compounds classified as probable human carcinogens by the EPA) for adults and<br />

children. Studies have estimated that dietary B2 PAH intakes in children are 24.8<br />

ng/kg/day or less, generally larger those associated with inhalation or non-dietary<br />

ingestion <strong>of</strong> soil and house dust. Recent research has indicated that the use <strong>of</strong> coal<br />

tar-based (CT) sealants on parking lots may be associated with increased concentrations<br />

<strong>of</strong> B2 PAHs in settled house dust (SHD) in nearby living spaces (compared<br />

with unsealed asphalt lots). We hypothesized that, for young children living in residences<br />

adjacent to CT-sealed parking lots, exposures to B2 PAHs through ingestion<br />

<strong>of</strong> SHD might surmount dietary intake as the primary route <strong>of</strong> exposure. Using default<br />

exposure assumptions <strong>of</strong> 17.4 kg body weight and 10 and 50 mg/day for dust<br />

ingestion rates, doses <strong>of</strong> 25.01 and 125.03 ng/kg/day B2 PAH were calculated for a<br />

4 year old child living in a residence next to a CT-sealed parking lot, compared to<br />

1.73 and 8.65 ng/kg/day for children living near unsealed asphalt parking lots.<br />

According to this screening-level exposure model, children in living spaces adjacent<br />

to parking lots sealed with CT-based products may be exposed to B2 PAHs primarily<br />

through ingestion <strong>of</strong> SHD.<br />

1230 DIRECT COMPARISON OF DRIED BLOOD SPOT (DBS)<br />

ANALYSIS TO PLASMA AND WHOLE BLOOD<br />

ANALYSIS IN TOXICOKINETIC STUDIES OF RATS.<br />

L. Patrone 1 , G. Liu 2 , H. M. Snapp 2 , A. Batog 1 , J. Valentine 1 , R. S.<br />

Mangipudy 1 , A. Tymiak 2 , Q. C. Ji 2 and M. E. Arnold 2 . 1 Drug Safety Evaluation,<br />

Bristol-Myers Squibb, New Brunswick, NJ and 2 Bioanalytical Sciences, Bristol-Myers<br />

Squibb, Lawrenceville, NJ.<br />

Dried blood spot (DBS) analysis is a method gaining recognition for obtaining<br />

drug exposure data. To evaluate the fidelity <strong>of</strong> DBS analysis compared to the accepted<br />

practice <strong>of</strong> plasma analysis, comparison <strong>of</strong> the data obtained by these methods<br />

is necessary. <strong>The</strong> primary objective <strong>of</strong> this presentation is to demonstrate how<br />

BMS is exploring DBS toxicokinetic applications in rats by directly comparing<br />

plasma to DBS from the same animal. In this study, 2 compounds were evaluated;<br />

BMS-X and Omeprazole (a marketed proton pump inhibitor). Twelve rats were<br />

evaluated for each compound, and 4 rats were used as controls to determine contamination<br />

potential. 300 ul blood was drawn from each rat. Blood was spotted directly<br />

from the collection tube onto the DBS cards in four 15 ul aliquots. <strong>The</strong> remaining<br />

blood was centrifuged to obtain plasma. <strong>The</strong> ratio <strong>of</strong> blood to plasma<br />

concentration was calculated and the “predicted” blood concentrations were obtained<br />

by applying the ratio to the plasma concentrations. Toxicokinetic curves<br />

were constructed by averaging the concentrations at each time point. Results obtained<br />

from DBS, blood, and plasma were consistent while liquid whole blood<br />

analysis was slightly more variable. Advantages <strong>of</strong> DBS include no need to centrifuge<br />

samples, easy sample storage and shipment, small sample volume, and easier<br />

sample preparation for analysis. Challenges include difficulties in assay development<br />

for hydrophilic compounds. Carry-over and cross contamination during sample<br />

analysis was not an issue. However, additional precaution is needed to prevent<br />

this when an assay has a low lower limit <strong>of</strong> quantitation (LLOQ).<br />

1231 DRIED BLOOD SPOT (DBS): A POTENTIAL<br />

APPROACH TO MONITORING DRUG EXPOSURE IN<br />

RAT FOETUSES.<br />

S. Cinelli 1 , F. Pastori 2 , R. Cicalese 3 , S. Villa 4 and G. Oberto 1 . 1 Scientific<br />

Direction, Research <strong>Toxicology</strong> Centre RTC, Pomezia - Rome, Italy, 2 Analytical<br />

Chemistry, Research <strong>Toxicology</strong> Centre, Pomezia - Rome, Italy, 3 <strong>Toxicology</strong>, Research<br />

<strong>Toxicology</strong> Centre, Pomezia - Rome, Italy and 4 Operative Direction, Research<br />

<strong>Toxicology</strong> Centre, Pomezia- Rome, Italy. Sponsor: J. Brightwell.<br />

Dried Blood Spot (DBS) is a promising technique to reduce blood sample volume<br />

during non-clinical and clinical studies. For this reason the technique has been extensively<br />

applied in the human paediatric population and could be used to monitor<br />

foetal drug exposure during non-clinical reprotoxicity studies. For this experiment<br />

oxacarbazepine was orally administered to pregnant rats and, following validation,<br />

the DBS technique was used to evaluate placental barrier crossing, testing blood<br />

from both dams and foetuses. Oxacarbazepine is an antiepileptic drug which is<br />

known to cross the placental barrier. Analytical methods were validated using Ultra<br />

Performance Liquid Chromatography and Tandem Mass Spectrometry (UPLC-<br />

MS/MS) on plasma samples, applying the traditional extraction procedure, and on<br />

whole blood spotted on DBS cards. Oxacarbazepine was administered to pregnant<br />

Sprague Dawley female rats by oral gavage during the gestation period. Blood samples<br />

were collected at necropsy from dams and foetuses. Blood taken from dams was<br />

used to generate both plasma and DBS samples to compare performance <strong>of</strong> the two<br />

procedures. Blood samples taken from foetuses were sufficient only to apply the<br />

DBS technique. <strong>The</strong> results <strong>of</strong> the described experiment, demonstrating placental<br />

transfer <strong>of</strong> oxacarbazepine, confirmed the applicability <strong>of</strong> DBS technique to evaluate<br />

drug levels in dams and litters during reprotoxicity studies.<br />

SOT 2011 ANNUAL MEETING 263

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!