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The Toxicologist - Society of Toxicology

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model compounds from three groups <strong>of</strong> ubiquitous environmental contaminants:<br />

quaternary ammonium compounds (QACs) used as disinfectants, polycyclic aromatic<br />

hydrocarbons (PAHs) released through use <strong>of</strong> fossil fuels, and sewage effluent,<br />

on embryos <strong>of</strong> the Japanese Medaka (*bital*Orizias latipes*eital*), using benzalkonium<br />

chloride (BAC), a high production volume chemical, as a model QAC,<br />

and benzo(α)pyrene (BaP) as a model PAH. We evaluated inhibition <strong>of</strong> multixenobiotic<br />

resistance (MXR) efflux pumps by quantifying accumulation <strong>of</strong> calcein-AM,<br />

and developmental toxicity by visually scoring developmental deficits and death.<br />

BAC inhibited MXR pump activity in a dose dependent manner, while BaP had no<br />

effect. Treated sewage effluent also inhibited pump activity, although adding BaP to<br />

effluent abolished the effect. BAC, BaP, and treated sewage effluent caused cranial<br />

facial, skeletal and heart deformities, as well as cardiac edema, all at sublethal concentrations.<br />

Co-exposure to BAC and BaP lead to greater than additive effects,<br />

while co-exposure to BaP had no significant effect on effluent toxicity. That BAC<br />

and sewage effluent are potent inhibitors <strong>of</strong> MXR pumps indicates exposure to<br />

these compounds can compromise this important defense system that limits cellular<br />

exposure to moderately hydrophobic contaminants or contaminant metabolites.<br />

<strong>The</strong> ability <strong>of</strong> these compounds to act as developmental toxicants is also noteworthy<br />

as is the enhanced toxicity observed with BaP exposure.<br />

2392 THE GULF OIL CRISIS: IMPACT ON WHALES.<br />

S. S. Wise 1, 2, 3 , I. Kerr 2, 4 , J. P. Wise 1, 2, 4 , C. F. Wise 1, 2, 4 , J. Wise 1, 2, 4 , C.<br />

Gianios 1, 2, 4 , M. Braun 1, 2, 4 , B. Wallace 4 , I. Glass 4 , R. Walker 4 , C. LaCerte 1, 2, 4 ,<br />

J. McKay 1, 2, 4 , T. Li Chen 1, 2, 4 , J. Martino 1, 2, 4 , G. Chapman 1, 2, 4 , R. Duffy 1, 2, 4 ,<br />

R. Leighton 1, 2, 4 , K. Joyce 1, 2, 4 and J. P. Wise 1, 2, 3 . 1 Wise Laboratory <strong>of</strong><br />

Environmental and Genetic <strong>Toxicology</strong>, University <strong>of</strong> Southern Maine, Portland, ME,<br />

2 Maine Center for <strong>Toxicology</strong> and Environmental Health, University <strong>of</strong> Southern<br />

Maine, Portland, ME, 3 Department <strong>of</strong> Applied Medical Science, University <strong>of</strong><br />

Southern Maine, Portland, ME and 4 Ocean Alliance, Lincoln, MA.<br />

<strong>The</strong> recent disaster in the Gulf <strong>of</strong> Mexico resulted in the release <strong>of</strong> 4.9 million barrels<br />

<strong>of</strong> oil and 2 million gallons <strong>of</strong> chemical dispersants. <strong>The</strong>se chemicals were used<br />

in unprecedented ways and amounts and the toxicity <strong>of</strong> them is poorly understood.<br />

<strong>The</strong> impact <strong>of</strong> the oil and dispersants on wildlife in the gulf is <strong>of</strong> significant concern.<br />

Many animals, including whales, fish and turtles, use the Gulf <strong>of</strong> Mexico as<br />

calving and spawning grounds. Of particular concern are whales as they are a key<br />

indicator species for the health <strong>of</strong> our oceans. Two resident populations include<br />

sperm whales and Bryde’s whales which are at particular risk because their population<br />

size is small. To address this crisis, we launched a voyage to assess the impacts<br />

<strong>of</strong> these pollutants on whale health. <strong>The</strong> research vessel Odyssey, a 93 foot ketch<br />

equipped with state-<strong>of</strong>-the art whale tracking, sampling equipment and cell culture<br />

facilities, was used for the voyage. Our scientific approach assessed 1) acute toxicity<br />

based on visual, acoustic and behavioral data, 2) subacute and chronic toxicity by<br />

measuring contaminant levels in whale biopsies, and 3) chronic toxicity by dosing<br />

cultured cells from these animals with petroleum products, dispersants and metals.<br />

In doing this early assessment a baseline set <strong>of</strong> toxicological data was established to<br />

compare it to similar efforts in the Atlantic as well as future years. <strong>The</strong> Voyage was<br />

supported by generous donations from the University <strong>of</strong> Southern Maine, <strong>The</strong><br />

Campbell Foundation, <strong>The</strong> Ocean Foundation, <strong>The</strong> Marisla Foundation and<br />

Quiznos among many other individual donors and supporters <strong>of</strong> the Wise<br />

Laboratory and Ocean Alliance.<br />

2393 IMPOSEX IN PLICOPURPURA PANSA<br />

(MOLLUSCA:NEOGASTROPODA) AS A POTENTIAL<br />

MARINE POLLUTION BIOINDICATOR IN NAYARIT<br />

AND SINALOA, MEXICO.<br />

D. Domínguez 1 , A. Patron 2, 1 , L. Robledo 1 , J. Velazquez 1 and B. Quintanilla 3, 1 .<br />

1 Laboratorio de Toxicologia, Universidad Autónoma de Nayarit, Tepic, Nayarit,<br />

Mexico, 2 Fisiologia, Universidad Autonoma de Mexico, DF, Mexico and 3 Toxicologia,<br />

Cinvestav, DF, Mexico.<br />

Imposex is a biomarker <strong>of</strong> marine species such as gastropods for the presence <strong>of</strong> a<br />

penis in females, and it has been used worldwide as a biomarker <strong>of</strong> exposure to<br />

organotin compounds (OTs). Samples <strong>of</strong> Plicopurpura pansa were collected and examined<br />

to assess the sex ratio, the presence <strong>of</strong> females with imposex and lipid peroxidation.<br />

<strong>The</strong>se populations were obtained from habitats exhibiting three presuming<br />

different levels <strong>of</strong> pollution (taking into account their proximity to pollutant<br />

places due to human activity) in Mexico such as Isabel Island and Santa Cruz, in<br />

Nayarit State, as well as Olas Altas, in Sinaloa State. Imposex in female mollusks<br />

was scored as the presence <strong>of</strong> a pseudopenis. Females and males were classified as<br />

those having normal characteristics. Lipid peroxidation was determined by the<br />

Thiobarbituric acid reactive species. <strong>The</strong> sex ratio <strong>of</strong> male:female in Olas Altas and<br />

Santa Cruz were 2:1 in both cases, whereas the sex ratio in Isabel Island was 1:1.<br />

<strong>The</strong> presence <strong>of</strong> imposex was 17.24% in Olas Altas, followed by 11.24% in Santa<br />

Cruz and 2.3% in Isabel Island. <strong>The</strong> lipoperoxidative damage was greater in organ-<br />

514 SOT 2011 ANNUAL MEETING<br />

isms from Olas Altas, followed by Santa Cruz and Isabel Island. According to these<br />

results, the more proximal to pollutant areas, the more oxidated the snails are, and<br />

the more number <strong>of</strong> imposex cases.<br />

2394 IN VITRO METABOLISM OF DIAZEPAM IN CHANNEL<br />

CATFISH (ICTALURUS PUNCTATUS).<br />

C. Overturf and D. Huggett. University <strong>of</strong> North Texas, Denton, TX.<br />

Many human pharmaceuticals have been detected in surface waters where they may<br />

bioconcentrate and pose adverse effects to aquatic life. Thus, the following study<br />

examined the in vitro metabolism <strong>of</strong> diazepam, a model benzodiazepine, in microsomal<br />

fractions <strong>of</strong> the liver from channel catfish to better determine its bioconcentration<br />

potential. In mammals, diazepam is metabolized to the active intermediates<br />

nordiazepam and temazepam via CYP2C19 and CYP3A4/5, respectively. Both intermediates<br />

are then further metabolized via CYP3A4 to the active metabolite oxazepam.<br />

This study attempted to investigate the loss <strong>of</strong> parent compound (diazepam),<br />

as well as the generation <strong>of</strong> active metabolites. Briefly, livers from catfish<br />

(n=3) were harvested and microsomal fractions were prepared. An NADPH regeneration<br />

system was used to simulate phase I reactions and 1000uM diazepam was<br />

added to the system. Samples were taken over a ninety-minute time period and<br />

placed in methanol to stop the reaction. <strong>The</strong> samples were then processed and analyzed<br />

using LC-MS/MS. A significant loss (14%) <strong>of</strong> parent compound was measured<br />

within forty-five minutes. Over the same ninety-minute period, both nordiazepam<br />

and temazepam were detected within fifteen minutes. <strong>The</strong>ir formation<br />

plateaued within thirty minutes at 35 parts per billion (ppb) and 102 ppb, respectively.<br />

Interestingly, oxazepam was not detected during the ninety-minute incubation<br />

period. This study shows that microsomal fractions <strong>of</strong> channel catfish liver<br />

contain the necessary enzymes for the metabolism <strong>of</strong> diazepam into two pharmacologically<br />

active intermediates. However, the time period may not have been sufficient<br />

for the generation <strong>of</strong> oxazepam to occur, or catfish enzyme systems may be<br />

unable to generate this secondary metabolite. Further studies will attempt to elucidate<br />

the metabolic pathway <strong>of</strong> diazepam metabolism and active metabolite formation<br />

in channel catfish.<br />

2395 QUEEN CONCH (STROMBUS GIGAS) REPRODUCTIVE<br />

DYSFUNCTION IN NEARSHORE AREAS OF THE<br />

FLORIDA KEYS – A POSSIBLE LINK TO CU AND ZN.<br />

D. Spade 1 , A. Feswick 1 , R. A. Glazer 2 , D. S. Barber 1 and N. D. Denslow 1 .<br />

1 Center for Environmental and Human <strong>Toxicology</strong>, University <strong>of</strong> Florida, Gainesville,<br />

FL and 2 Fish and Wildlife Research Institute, Florida Fish and Wildlife Conservation<br />

Commission, Marathon, FL.<br />

In the Florida Keys, queen conchs (Strombus gigas) residing <strong>of</strong>fshore (OS) develop<br />

gonads and are capable <strong>of</strong> reproduction, while near-shore (NS) conchs lack sufficient<br />

gonadal development for reproduction. A custom queen conch microarray<br />

(GEO accession GPL8934) was used to study differences in gene expression between<br />

OS and NS conch. 257 transcripts were differentially regulated in testis,<br />

1368 in ovary, and 1153 in the digestive gland <strong>of</strong> females (ANOVA, p

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