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1.
Aquat Toxicol ; 213: 105204, 2019 Aug.
Article in English | MEDLINE | ID: mdl-31185427

ABSTRACT

Previous toxicological investigations of the insensitive munition (IM), 3-nitro-1,2,4-triazol-5-one (NTO), demonstrated histopathological and physiological impacts in mammalian testes. The implications of these findings for fish was unknown, therefore we investigated the effects of chronic (21 day) exposures to NTO and an NTO-containing IM formulation called IMX-101 (composed of 2,4-dinitroanisole (DNAN), nitroguanidine (NQ), and NTO) in adult male fathead minnows to assess if impacts on testes were conserved. The NTO exposure caused no significant mortality through the maximum exposure concentration (720 mg/L, measured), however NTO elicited testicular impacts causing significant asynchrony in spermatogenesis and necrosis in secondary spermatocytes at the two highest exposure concentrations (383 mg/L and 720 mg/L) and testicular degeneration at the highest exposure. Microarray-based transcriptomics analysis identified significant enrichment of steroid metabolism pathways and mTORC-signal control of spermatogonia differentiation in NTO exposures each having logical connections to observed asynchronous spermatogenesis. Additionally, NTO impaired transcriptional expression for genes supporting sperm structural and flagellar development including sperm-associated antigen 6 (Spag6). These functional transcriptomic responses are hypothesized contributors to impacted reproductive physiology in NTO exposures that ultimately lead to reductions in spermatozoa. In contrast to NTO, the IMX-101 formulation elicited significant mortality at the two highest exposure concentrations of 25.2 and 50.9 mg/L (DNAN nominal + NTO measured + NQ measured). Unlike NTO and NQ, the DNAN component of the IMX-101 formulation underwent significant transformation in the 21d exposure. From previous investigations, neither NTO nor NQ caused mortality in fish at >1000 mg/L suggesting that mortality in the present study arose from DNAN / DNAN-attributable transformation products. The 12.6 mg/L IMX-101 exposure caused significant sublethal impacts on testes including sperm necrosis, interstitial fibrosis, and Sertoli-like cell hyperplasia. Transcriptional profiles for IMX-101 indicated significant enrichment on multiple signaling pathways supporting spermatogenesis, mitosis / meiosis, and flagellar structure, all logically connected to observed sperm necrosis. Additionally, pronounced transcriptional increases within the PPARα-RXRα pathway, a known DNAN target, has been hypothesized to correspond to Sertoli cell hyperplasia, presumably as a compensatory response to fulfill the nurse-function of Sertoli cells during spermatogenesis. Overall, the transcriptional results indicated unique molecular responses for NTO and IMX-101. Regarding chemical hazard, NTO impacted testes and impaired spermatogenesis, but at high exposure concentrations (≥ 192 mg/L), whereas the IMX-101 formulation, elicited mortality and impacts on reproductive physiology likely caused by DNAN and its transformation products present at concentrations well below the NTO-component concentration within the IMX-101 mixture formulation.


Subject(s)
Anisoles/toxicity , Cyprinidae/physiology , Nitro Compounds/toxicity , Testis/physiology , Triazoles/toxicity , Animals , Cyprinidae/genetics , Male , Principal Component Analysis , Reproduction/drug effects , Spermatogenesis , Testis/drug effects , Testis/pathology , Transcriptome/genetics , Water Pollutants, Chemical/toxicity
2.
Ecotoxicol Environ Saf ; 154: 245-254, 2018 Jun 15.
Article in English | MEDLINE | ID: mdl-29476974

ABSTRACT

We examined gonads and thyroid glands of Gulf killifish (Fundulus grandis) 1yr after the Deepwater Horizon oil spill. F. grandis were trapped from two impacted sites in Barataria Bay (Bayou St. Denis, Bay Jimmy) and an un-impacted site in East Texas (Sabine Pass). The greatest number of F. grandis were collected at Sabine Pass. F. grandis collected at Bayou St. Denis were smaller and had smaller Fulton condition factor scores than fish collected at Sabine Pass. Sex ratios were biased roughly 2:1 in favor of females at Sabine Pass and Bayou St. Denis. Gonad-somatic index (GSI) in males from Sabine Pass was double that of fish from Bay Jimmy while germinal epithelium thickness of the testes was 2.7 fold smaller in males from the impacted site. GSI and oocyte diameters in females from Bayou St. Denis were significantly smaller than females from Bay Jimmy or the reference site. There were no differences in thyroid follicle cell height. While total polyaromatic hydrocarbons at the impacted sites were no different from the reference site, the impacted sites did have greater concentrations of benzo[a]pyrene in sediment pore water. The finding of smaller GSI and testicular germinal epithelium in males from an impacted site suggest that exposure to a combination of oil and dispersants may adversely impact testicular function.


Subject(s)
Environmental Monitoring/methods , Fundulidae/growth & development , Gonads/drug effects , Petroleum Pollution/adverse effects , Thyroid Gland/drug effects , Water Pollutants, Chemical/toxicity , Animals , Bays/chemistry , Female , Gonads/pathology , Gulf of Mexico , Louisiana , Male , Petroleum Pollution/analysis , Thyroid Gland/pathology , Water Pollutants, Chemical/analysis
3.
Breast Cancer Res Treat ; 118(1): 33-43, 2009 Nov.
Article in English | MEDLINE | ID: mdl-18855134

ABSTRACT

To investigate the therapeutic effect of methylselenocysteine (MSC) combined with tamoxifen in MCF-7 breast cancer xenograft and the underlying mechanisms. MCF-7 breast cancer xenograft was established in ovariectomized female athymic nude mice and treated with tamoxifen and/or MSC. Tumor size was measured twice a week. Immunohistochemistry and TUNEL assays were used to measure ERalpha expression, ERalpha target genes (progesterone receptor (PR) and cyclin D1 expression), Ki-67 index, apoptosis and microvessel density. Combined treatment with tamoxifen and MSC synergistically inhibited tumor growth compared to MSC alone and tamoxifen alone. MSC alone or MSC + tamoxifen significantly reduced ERalpha, PR and cyclin D1, Ki67 index and microvessel density while increasing apoptosis in tumor tissues. These findings demonstrate synergistic growth inhibition of ERalpha positive breast cancer xenografts by combination of tamoxifen with organic selenium compounds. Organic selenium may provide added benefit when combined with tamoxifen in adjuvant therapy or prevention.


Subject(s)
Adenocarcinoma/drug therapy , Angiogenesis Inhibitors/therapeutic use , Antineoplastic Combined Chemotherapy Protocols/therapeutic use , Apoptosis/drug effects , Breast Neoplasms/drug therapy , Cysteine/analogs & derivatives , Estradiol , Neoplasms, Hormone-Dependent/drug therapy , Neovascularization, Pathologic/drug therapy , Organoselenium Compounds/pharmacology , Adenocarcinoma/blood supply , Adenocarcinoma/metabolism , Adenocarcinoma/pathology , Animals , Breast Neoplasms/blood supply , Breast Neoplasms/metabolism , Breast Neoplasms/pathology , Cell Division/drug effects , Cyclin D1/biosynthesis , Cyclin D1/genetics , Cysteine/administration & dosage , Cysteine/pharmacology , Drug Synergism , Estradiol/toxicity , Estrogen Receptor alpha/biosynthesis , Estrogen Receptor alpha/genetics , Female , Gene Expression Regulation, Neoplastic/drug effects , Humans , Mice , Mice, Nude , Neoplasm Proteins/biosynthesis , Neoplasm Proteins/genetics , Neoplasms, Hormone-Dependent/blood supply , Neoplasms, Hormone-Dependent/metabolism , Neoplasms, Hormone-Dependent/pathology , Organoselenium Compounds/administration & dosage , Random Allocation , Receptors, Progesterone/biosynthesis , Receptors, Progesterone/genetics , Selenocysteine/analogs & derivatives , Specific Pathogen-Free Organisms , Tamoxifen/administration & dosage , Xenograft Model Antitumor Assays
4.
Chemosphere ; 58(9): 1283-91, 2005 Mar.
Article in English | MEDLINE | ID: mdl-15667848

ABSTRACT

The United States Environmental Protection Agency (USEPA) has pursued the estimation of risk of adverse health effects from exposure to chemical mixtures since the early 1980s. Methods used to calculate risk estimates of mixtures were often based on single chemical information that required assumptions of dose-addition or response-addition and did not consider possible changes in response due to interaction effects among chemicals. Full factorial designs for laboratory studies can produce interactions information, but these are expensive to perform and may not provide the information needed to evaluate specific environmentally relevant mixtures. In this research, groups of Japanese medaka (Oryzias latipes) embryos were exposed to binary mixtures of benzene and toluene as well as to each of these chemicals alone. Endpoint specific dose-response models were built for the hydrocarbon mixture under an assumption of dose-additivity, using the single chemical dose-response information on benzene and toluene. The endpoints included heart rate, heart rate progression, and lethality. Results included a synergistic response for heart rate at 72 h of development, and either additivity or antagonism for all other endpoints at 96 h of development. This work uses an established statistical method to evaluate the toxicity of an environmentally relevant mixture to ascertain whether interaction effects are occurring, thus providing additional information on toxicity.


Subject(s)
Benzene/toxicity , Heart Rate/drug effects , Heart/embryology , Oryzias/embryology , Toluene/toxicity , Water Pollutants, Chemical/toxicity , Animals , Drug Interactions , Female , Heart/drug effects , In Vitro Techniques , Models, Statistical
5.
Sci Total Environ ; 302(1-3): 109-26, 2003 Jan 20.
Article in English | MEDLINE | ID: mdl-12526903

ABSTRACT

Between 1990 and 1994, samples of three shellfish species (i.e. blue crab, Callinectes sapidus;crayfish, Procambarus acutis; and river shrimp, Macrobrachium ohionii) and 16 fish species and were collected at six sites along the lower Mississippi River by the Louisiana Department of Environmental Quality, Office of Water Resources in coordination with the US Environmental Protection Agency. The fish species included: bigmouth buffalo (Ictiobus cyanellus); blue catfish (Ictalurus furcatus); carp (Cyprinus carpio); channel catfish (Ictalurus punctatus); cobia (Rachycentron canadum); flathead catfish (Pylodictis olivaris); freshwater drum (Aplodinotus grunniens); largemouth bass (Micropterus salmoides); long nose gar (Lepisosteus osseus); red drum (Sciaenops ocellatus); red snapper (Lutjanus campechanus); smallmouth buffalo (Ictiobus bubalus); spotted gar (Lepisosteus oculatus); striped bass (Morone saxatilis); white bass (Morone chrysops); and white crappie (Pomoxis annularis). Organic compound and heavy metal concentrations were measured in 161 composite fish tissue samples where each composite included three to 10 individual fish. Nineteen chemicals, found at measurable levels in sample tissues, were used in calculations of lifetime excess cancer and non-cancer risks due to fish consumption. We calculated: 574 chemical-specific cancer risks; 41 total cancer risks; and 697 margins of exposure based on a consumption rate of one 8-ounce meal per week (0.032 kg/day), a body weight of 70 kg and reported cancer potency factors and reference doses. We identified nine species of concern (blue catfish, carp, channel catfish, cobia, crayfish, flathead catfish, red drum, spotted gar and striped bass) based on total cancer risk greater than 10(-4) or margin of exposure greater than 1, and whether or not samples collected in subsequent years resulted in lower risks. The compounds primarily responsible for the elevated risks were aldrin, dieldrin, alpha-benzene hexachloride, gamma-benzene hexachloride, heptachlor epoxide, arsenic and mercury.


Subject(s)
Carcinogens/analysis , Fishes , Food Contamination , Metals, Heavy/analysis , Shellfish , Water Pollutants, Chemical/analysis , Animals , Body Weight , Carcinogens/adverse effects , Humans , Louisiana , Metals, Heavy/adverse effects , Neoplasms/etiology , Risk Assessment , Tissue Distribution , Water Pollutants, Chemical/adverse effects
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