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.

functionality <strong>of</strong> photosystem II and an increase on lipid peroxidation were detected.<br />

Furthermore, the study <strong>of</strong> thermoluminescence emissions is a useful technique<br />

to study the effects <strong>of</strong> environmental chemicals on photosynthetic organisms.<br />

2386 TISSUE DISTRIBUTION OF MERCURY IN ALASKA<br />

SCULPIN SPECIES.<br />

S. Bhojwani, C. Lieske and T. O’Hara. University <strong>of</strong> Alaska Fairbanks,<br />

Fairbanks, AK.<br />

Mercury contamination <strong>of</strong> marine species is a big concern for subsistence hunters as<br />

well as fish consumers today. Mercury accumulates in marine animals and is associated<br />

with many negative health impacts including neurotoxicity. For this study, select<br />

tissue samples from nineteen subsistence-caught sculpin species were taken,<br />

freeze dried, and analyzed for total mercury (THg) via a DMA-80 (Direct Mercury<br />

Analyzer-80) in order to determine the differences in mercury within and across<br />

different tissue types (liver, muscle, heart and kidney). Additionally, differences in<br />

mercury deposition within skeletal muscles were assessed. Wet weight THg concentrations<br />

ranged from 0.58 to 0.935 ppm in the skeletal muscle, 0.015 to 0.39 ppm<br />

in the liver, 0.017 to 0.24 ppm in the kidney, and from 0.016 to 0.17 ppm in the<br />

heart. It was noted that as fish size increased, the THg present in the fish likewise<br />

increased. Significant differences were noted between internal organs and muscle<br />

tissue, with THg concentrations in muscle greater than THg in the internal organs<br />

(liver, heart and kidney). A significant difference between the mean mercury content<br />

across the four muscle samples was detected, with the mean mercury at the<br />

caudal end greater than the mean mercury at the most cranial end for 18 <strong>of</strong> 19 fish.<br />

However, the observed difference may not be biologically significant due to the heterogeneity<br />

<strong>of</strong> the muscle samples. <strong>The</strong>se data suggest that the internal organs <strong>of</strong><br />

these sculpin species have much less mercury content in comparison to the muscle<br />

tissue, and that fish that are small or <strong>of</strong> average size may be safer to consume than<br />

those <strong>of</strong> larger sizes.<br />

2387 PROTEOMIC ANALYSIS OF A MODEL FISH SPECIES<br />

EXPOSED TO INDIVIDUAL PESTICIDES AND A<br />

BINARY MIXTURE.<br />

A. D. Biales, D. C. Bencic, K. Blocksom, D. L. Lattier, R. Flick and L. Jim.<br />

ORD NERL, U.S. EPA, Cincinnati, OH. Sponsor: H. Choudhury.<br />

Pesticides are nearly ubiquitous in surface waters <strong>of</strong> the United States, where they<br />

<strong>of</strong>ten are found as mixtures. <strong>The</strong> molecular mechanisms underlying the toxic effects<br />

<strong>of</strong> sub-lethal exposure to pesticides as both individual and mixtures are unclear. <strong>The</strong><br />

current work aims to identify and compare differentially expressed proteins in<br />

brains <strong>of</strong> male fathead minnows (Pimephales promelas) exposed for 72 h to permethrin<br />

(7.5 μg/L), terbufos (57.5 μg/L) and a binary mixture <strong>of</strong> both. Twenty-four<br />

proteins were found to be differentially expressed among all three treatments relative<br />

to the control using an ANOVA followed by a Dunnett’s post-hoc test (p ≤<br />

0.05). One protein was found to be differentially expressed among all treatment<br />

groups and one protein was in common between the terbufos and the mixture<br />

group. Fifteen spots were successfully sequenced using LC-MS/MS sequencing.<br />

Proteins associated with the ubiquitin-proteasome system, glycolysis, the cytoskeleton<br />

and hypoxia were enriched. As a second objective, we attempted to establish<br />

protein expression signatures (PES) for individual permethrin and terbufos exposures.<br />

We were unable to generate a useable PES for terbufos; however, the permethrin<br />

PES was able to distinguish between control and permethrin-exposed individuals<br />

in an independent experiment with an accuracy <strong>of</strong> 87.5%. This PES also<br />

accurately classified permethrin exposed individuals when the exposure occurred as<br />

part <strong>of</strong> a mixture. <strong>The</strong> identification <strong>of</strong> proteins differentially expressed as a result <strong>of</strong><br />

pesticide exposure represent a step forward in the understanding <strong>of</strong> mechanisms <strong>of</strong><br />

toxicity <strong>of</strong> permethrin and terbufos. <strong>The</strong>y also allow a comparison <strong>of</strong> molecular responses<br />

<strong>of</strong> the binary mixture to single exposures. <strong>The</strong> permethrin PES is the first<br />

step in establishing a method to determine exposures in real-world scenarios.<br />

2388 TRIBUTYLTIN (TBT), AN ENDOCRINE DISRUPTOR IN<br />

ZEBRAFISH.<br />

C. L. McGinnis and J. F. Crivello. Physiology and Neurobiology, University <strong>of</strong><br />

Connecticut, Storrs, CT.<br />

Tributyltin (TBT) is an antifouling agent that has been implicated in the masculinization<br />

<strong>of</strong> fish species worldwide; however, its masculinizing mechanism is not fully<br />

understood. We have examined the actions <strong>of</strong> TBT as an endocrine disruptor on<br />

three different endpoints in zebrafish (Danio rerio): 1) directly on nuclear receptors<br />

in HeLa cells, 2) on enzymatic activities <strong>of</strong> hepatic acylated and sulfated testosterone,<br />

and 3) on the expression <strong>of</strong> androgenic and estrogenic developmental markers<br />

in vivo. Zebrafish estrogen receptor (zfERα, zfERβ1 and zfERβ2) dependent<br />

activity was inhibited by TBT in a dose dependent manner, with an ED50 between<br />

5nM and 50nM. TBT had no effect on zebrafish androgen receptor (zfAR); however,<br />

TBT inhibited zebrafish aromatase (zfCYP19b-luc) dependent activity in a<br />

dose dependent manner. In HeLa cells, TBT elicited a dose dependent activation <strong>of</strong><br />

the peroxisome proliferator-activated receptor gamma (PPARγ) and retinoid X receptor<br />

alpha (RXRα) heterodimer, mediated through RXRα. In zebrafish exposed<br />

to 1 to 5mg/kg TBT, there was increased liver sulfotransferase activity and decreased<br />

acyl-CoA testosterone acyltransferase activity. Real-time PCR analysis <strong>of</strong><br />

sexual differentiation markers in zebrafish exposed to TBT revealed tissue-specific<br />

responses. TBT overall has a masculinizing effect, but the masculinizing effect may<br />

be tempered by the metabolism <strong>of</strong> TBT to dibutyltin (DBT).<br />

2389 THE EFFECTS OF COPPER PYRITHIONE ON<br />

DEVELOPING ZEBRAFISH EMBRYOS.<br />

K. M. Almond and L. D. Trombetta. Pharmaceutical Sciences, St. John’s University,<br />

Queens, NY.<br />

Copper pyrithione, an active component in antifouling biocides predominantly<br />

found in marine paints, has been shown to cause anomalies during early development<br />

<strong>of</strong> mummichogs (Fundulus heteroclitus). Since a strict regulatory use <strong>of</strong><br />

organotins as antifouling agents has been imposed, a frequent substitute by foreign<br />

markets has been the use <strong>of</strong> metal pyrithiones, principally zinc and copper.<br />

Zebrafish (Danio rerio) embryos were exposed within the first hour after fertilization<br />

to increasing concentrations <strong>of</strong> copper pyrithione (2, 4, 8, 12, 16, 32 and 64<br />

μg/l) for 24 hours. Morphological abnormalities at 30, 60, and 120 hours post fertilization<br />

were recorded. Hatchability was measured at every 12 hours for 5 days.<br />

Following the 24 hour exposure, results show morphological abnormalities, particularly<br />

<strong>of</strong> the notochord at concentrations <strong>of</strong> 12 μg/l and higher. <strong>The</strong> notochord was<br />

severely twisted and abnormally segmented as the concentrations increased.<br />

Distortions <strong>of</strong> the notochord began in the tail at the lower concentrations and proceeded<br />

rostrally as doses increased. Edema was observed in the cardiac and yolk sac<br />

regions at 12 and 16 μg/l concentrations. Hatching rate decreased in a dose dependent<br />

manner. At 120 hours post fertilization, 47 percent <strong>of</strong> embryos hatched,<br />

while all <strong>of</strong> the controls hatched by 96 hours post fertilization. Copper pyrithione<br />

has shown to be toxic to zebrafish at concentrations <strong>of</strong> 12 μg/l and higher. <strong>The</strong> abnormalities<br />

and deformities observed in fish larvae would significantly decrease<br />

their chance <strong>of</strong> survival in non-controlled environments.<br />

2390 TISSUE SPECIFIC EXPRESSION OF ORGANIC ANION<br />

TRANSPORTING POLYPEPTIDES IN NATIVE FISH<br />

SPECIES.<br />

K. Steiner 1 , K. Shigehiro 2 , A. Meyer 2 and D. R. Dietrich 1 . 1 Human &<br />

Environmental <strong>Toxicology</strong>, University <strong>of</strong> Konstanz, Konstanz, Germany and 2 Zoology<br />

and Evolutionary Biology, University <strong>of</strong> Konstanz, Konstanz, BW, Germany.<br />

Microcystins (MCs) are naturally occurring toxins that are produced by many<br />

species <strong>of</strong> cyanobacteria. MCs are cyclic heptapeptide cyanotoxins with >80 structural<br />

variants and a molecular weight ranging from 900 to 1100 Da. Toxic<br />

cyanobacterial blooms in aquatic ecosystems have been associated with dramatic<br />

changes in species distribution. It is hypothesized that the bioavailability <strong>of</strong> MCs,<br />

via specific MC transporting organic anion transporting polypeptides (Oatps), governs<br />

the susceptibility <strong>of</strong> different species and life-stages and thus the downstream<br />

adverse effects on organisms and ecosystems more strongly than the level <strong>of</strong> MC<br />

concentrations alone in the ambient environment. Consequently the presence <strong>of</strong><br />

Oatps and their organ specific expression in fish may be key to understanding the<br />

biological effects <strong>of</strong> MCs. Recently verified short Oatps from native fish species<br />

were sequenced using RACE PCR and phylogenetically analyzed in order to identify<br />

specific Oatp subtypes, which were used for designing gene specific primers.<br />

<strong>The</strong> improved primers were employed to analyze the Oatp subtype expression pr<strong>of</strong>ile<br />

in different fish tissues via real-time quantitative PCR. <strong>The</strong> different sequences<br />

obtained were verified as Oatp by BLAST and elongated using RACE PCR. A sequence<br />

identified as Oatp1d1 was expressed in a tissue-dependent manner, suggesting<br />

an organ-specific transport <strong>of</strong> MC.<br />

2391 INTERACTIVE EFFECTS OF BENZO(α)PYRENE,<br />

BENZALKONIUM CHLORIDE, AND SEWAGE<br />

EFFLUENT ON MEDAKA EMBRYOS.<br />

A. McElroy and J. Gondek. School <strong>of</strong> Marine and Atmospheric Sciences, Stony Brook<br />

University, Stony Brook, NY. Sponsor: R. Di Giulio.<br />

Chemical mixtures represent a common stressor to organisms, yet traditional toxicological<br />

approaches rarely examine interactive effects <strong>of</strong> contaminants found in the<br />

environment. For aquatic organisms, particularly those living in urban watersheds,<br />

exposure to mixtures from sewage inputs, surface run-<strong>of</strong>f, and contaminated sediments<br />

is a chronic problem. We evaluated the individual and combined effects <strong>of</strong><br />

SOT 2011 ANNUAL MEETING 513

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

Saved successfully!

Ooh no, something went wrong!