Cave (Petrochelidon fulva) and cliff swallows (Petrochelidon pyrrhonota) were collected along the Rio Grande and evaluated as potential indicators of environmental contamination. The Rio Grande receives toxic substances from agricultural, industrial, municipal, and non-point sources; consequently, high levels of contaminants have been detected in birds, mammals, fishes and sediments. Swallows were obtained from 8 sites between Brownsville and El Paso, as well as from a reference site in Burleson County, 320 miles north of the nearest site of the Rio Grande. Blood samples were analyzed by flow cytometry, a technique that allows the detection of DNA damage in blood and other tissues. Plasma samples were analyzed for thyroid hormones using a radioimmunoassay technique. Organochlorines and trace metal analysis was limited to a few samples. DDE and PCB levels were below levels known to cause reduced hatching, embryo mortality, and deformities, Hg, Pb, and As were below detection, and Se, Ni and Cr concentrations were lower than levels known to cause harm in birds. Neither species showed sex-related differences in chromosome damage. Cave swallows from the Del Rio area had the highest levels of DNA variation, which may be indicative of DNA damage, possibly from PAHs exposure. Previous studies indicate that sediment samples from tributaries near Del Rio have high levels of chromium compared to other sites along the Rio Grande. A significant increase in DNA variation between sampling years was detected in cave swallows from Llano Grande Lake. Wildlife samples collected from Llano Grande Lake have recorded high levels of DDE and PCBs; in addition, this urban/agricultural contaminant sink appears to be affected by PAH exposure. T3 levels were below the detection limit of the radioimmunoassay. There were no gender related differences in T4 levels in cave swallows. Cave swallows sampled from Laredo had significantly higher T4 levels than those from birds at other sites during 1999. It was not possible to determine thyroid hormone disruption in plasma samples. Thyroid hormone and flow cytometry data were useful in establishing baseline data. Areas of concern based on genotoxic data include Llano Grande Lake, Del Rio, and El Paso.

There is a growing interest in assessing the neurotoxic potential and endocrine disrupting properties of perfluoroalkyl compounds (PFCs). Several studies have reported in vitro and in vivo effects related to neuronal development, neural cell differentiation, pre- and post- natal development and behaviour. PFC exposure altered hormone levels (e.g. thyroid hormone, estrogen, and testosterone) and the expression of hormone-responsive genes in mammalian and aquatic species. Hormone-mediated events are critical in central nervous system development and function, especially those controlled by thyroid hormones (THs). The studies presented in this thesis are the first to assess the effects of PFCs on primary cultures of neuronal cells in two avian species; the domestic chicken (Gallus domesticus) and herring gull (Larus argentatus). The following TH-responsive genes were examined using real-time RT-PCR: type II iodothyronine 5’-deiodinase (D2), D3, transthyretin (TTR), neurogranin (RC3), octamer motif binding factor (Oct-1), and myelin basic protein (MBP). Several PFCs were shown to alter mRNA expression levels of genes associated with the TH pathway in avian neuronal cells. It was determined that short-chained PFCs (<8 carbons) altered the expression of TH-responsive genes to a greater extent than long-chained PFCs (≥8 carbons). Although several significant changes in mRNA expression were observed in TH-responsive genes following PFC exposure in chicken embryonic neuronal (CEN) cells (Chapter 2), there were fewer changes in herring gull embryonic neuronal (HGEN) cells (Chapter 3). The mRNA levels of D2, D3, TTR, and RC3 were altered following treatment with several short-chained PFCs in CEN cells. Oct-1 and RC3 expression were induced following treatment with several short-chained PFCs in HGEN cells. These studies are the first to report that PFC exposure alters mRNA expression in primary cultures of avian neuronal cells and provide insight into the possible mechanisms of action of PFCs in the avian brain.

Perfluoroalkyl acids (PFAAs) are a family of synthetic substances used in a wide variety of consumer and industrial applications, including non-stick and stain-resistant products. PFAAs, specifically perfluorinated sulfonates and carboxylates, are chemically stable and virtually non-biodegradable in the environment. In recent years, PFAAs have been detected in tissues and blood of humans and wildlife. Furthermore, PFAAs have a tendency to bioaccumulate and biomagnify in biota. Perfluorooctane sulfonate and perfluorooctanoate are known to be toxic when animals are exposed to environmentally-relevant levels, but scientists and regulators are challenged with determining and predicting their modes of action. There is some evidence to suggest that PFAAs can impact the thyroid hormone (TH) pathway and neurodevelopment. The studies presented in this thesis investigated the developmental effects and potential modes of action of newer PFAAs that are being introduced into the global market place. Egg injection experiments were performed in domestic chicken (Gallus gallus domesticus) embryos to assess the in ovo toxicity of perfluorohexane sulfonate (PFHxS) and perfluorohexanoate (PFHxA) during development. Real-time RT-PCR was used to measure the transcription of candidate genes in the liver and cerebral hemisphere of day 21-22 embryos. Candidate genes were selected based on their responsiveness to PFAA exposure in an in vitro screening assay conducted previously. In ovo exposure to PFHxS decreased embryo pipping success and overall growth at 38,000 ng/g; several orders of magnitude higher than concentrations reported in wild bird eggs. The expression of TH-responsive genes, including type II and III 5'-deiodinase, neurogranin, and octamer motif binding factor 1, were induced. In addition, PFHxS diminished free thyroxine (T4) levels in plasma. PFHxA had no affect on pipping success, gene expression or T4 levels in chicken embryos at the doses assessed. The transcriptional profiles in the cerebral hemisphere of chicken embryos exposed to 890 and 38,000 ng/g PFHxS were compared to a solvent control using microarray technology. The expression of 78 different genes were significantly altered (fold change > 1.5, p < 0.001) by PFHxS. Functional analysis showed that PFHxS affected genes involved in tissue development and morphology and cellular assembly and organization. Pathway and interactome analysis suggested that gene expression may be affected through integrin receptors and signaling pathways via TH–dependent and –independent modes of action. It is expected that the findings presented in this thesis will be of general relevance and importance to regulatory agencies and of interest to research scientists and risk assessors.

There is a growing interest in assessing the neurotoxic potential and endocrine disrupting properties of perfluoroalkyl compounds (PFCs). Several studies have reported in vitro and in vivo effects related to neuronal development, neural cell differentiation, pre- and post- natal development and behaviour. PFC exposure altered hormone levels (e.g. thyroid hormone, estrogen, and testosterone) and the expression of hormone-responsive genes in mammalian and aquatic species. Hormone-mediated events are critical in central nervous system development and function, especially those controlled by thyroid hormones (THs). The studies presented in this thesis are the first to assess the effects of PFCs on primary cultures of neuronal cells in two avian species; the domestic chicken (Gallus domesticus) and herring gull (Larus argentatus). The following TH-responsive genes were examined using real-time RT-PCR: type II iodothyronine 5’-deiodinase (D2), D3, transthyretin (TTR), neurogranin (RC3), octamer motif binding factor (Oct-1), and myelin basic protein (MBP). Several PFCs were shown to alter mRNA expression levels of genes associated with the TH pathway in avian neuronal cells. It was determined that short-chained PFCs (<8 carbons) altered the expression of TH-responsive genes to a greater extent than long-chained PFCs (≥8 carbons). Although several significant changes in mRNA expression were observed in TH-responsive genes following PFC exposure in chicken embryonic neuronal (CEN) cells (Chapter 2), there were fewer changes in herring gull embryonic neuronal (HGEN) cells (Chapter 3). The mRNA levels of D2, D3, TTR, and RC3 were altered following treatment with several short-chained PFCs in CEN cells. Oct-1 and RC3 expression were induced following treatment with several short-chained PFCs in HGEN cells. These studies are the first to report that PFC exposure alters mRNA expression in primary cultures of avian neuronal cells and provide insight into the possible mechanisms of action of PFCs in the avian brain.

Thyroid hormones are well known important to be in development and growth in birds and that signaling of thyrotropin (TSH) regulates the photo induced seasonal reproduction. A mutation at the thyroid stimulating hormone receptor (TSHR) gene in domestic breeds of chicken could be involved in the release of the photoperiodic regulation. Furthermore, TSH can affect a wide range of domestication related phenotypes, such as behaviour, growth rate and pigmentation. The aim of this study was to investigate the behaviours expressed in the different genotypes on the TSHR gene in chickens. Four standard tests were conducted, aerial predator, fear of human, social dominance and tonic immobility. An advanced intercross line of chickens between red junglefowl and White leghorn was used. Male domestic type chickens explored more, showed more less fear behaviours and showed least fear behaviours in the fear of human test. Increased activity and flight response has been interpreted as a lower fear response, which is in line with this study. The wild type chickens showed more social dominance than domestic type chickens which are in line with previous results. In tonic immobility there was a difference between the wild type male and heterozygous male chickens in latency until first head movement. The conclusion of this study is that there is a difference between the wild type and domestic type chickens. This indicates that the TSHR gene is involved in behavioural changes during domestication, but whether it is due to passive or active selection is the question.

The feasibility of using a thyroid uptake counter, normally used to measure the uptake of radioactive iodine in thyroid treatments, to assay radioactivity deposited in a persons lungs has been investigated. Variations in radioactive material distributions in the lungs, the response of the detector system to radionuclides of interest to homeland security, and the change in detection efficiency due to the varying thicknesses of intervening tissue of the victims have been simulated using the Monte Carlo N-Particle transport code (MCNP5) developed by Los Alamos National Laboratory. Point source and homogenously distributed models were created for Co-60, I-131, Cs-137, Ir-192, and Am-241 sources to simulate radiation transport between the lungs of multiple phantom models representing children and adults and the radiation detection system. To validate the simulations undertaken, the response of the counter to radiation sources in air and behind layers of Lucite have been modeled and compared to measured results.

This study investigated the effect of chronic alcohol exposure on the responses of the maternal hypothalamus-pituitary adrenal axis (HPA-axis) and thyroid hormones throughout gestation using an ovine model. Maternal plasma concentrations of ACTH, cortisol and the thyroid hormones T3, free T4 and total T4 were determined in response to infusion of 0.75, 1.25 and 1.75 g/kg alcohol. Maternal endocrine responses to alcohol administration have been investigated before in rodent models. However, this is the first study using a large animal model (sheep), in which all three human trimester equivalents occur in utero. Different concentrations of alcohol were administered intermittently from gestational day 4 to 132 in a pattern that modeled human binge drinking during pregnancy. Maternal blood samples were collected on specific days (GD 6, 40, 90, 132) and at multiple time-points (0, 0.5, 1, 1.5, 2, 6, 24 hours) and were analyzed to determine blood alcohol concentrations (BACs) and ACTH, cortisol, free T4, total T4 and T3 plasma concentrations. Alcohol readily permeates the placenta and can directly affect fetal cells and tissues. Alcohol also causes endocrine imbalances in the mother and interferes with maternal-fetal hormonal interactions and the mother’s ability to maintain a healthy pregnancy, thus also indirectly affecting fetal development. Sheep receiving either 0.75, 1.25 or 1.75 g/kg alcohol achieved peak BAC values of 93 + 5, 126 + 5 and 183 + 5 respectively. Alcohol exposure resulted in increased plasma ACTH and cortisol concentrations peaking at 2 hours after beginning of the infusion and returning to baseline values at 6 hours after beginning of the infusion. There was no effect of alcohol on any of the plasma thyroid hormone concentrations. Thyroid hormone concentrations changed as a result of progressing pregnancy. Plasma concentrations of total T4 and free T4 were higher on gestational days 6 and 40 compared to GDs 90 and 132, and plasma T3 concentrations were highest on GD 6. The results of this study show that alcohol stimulates the HPA-axis in a dose dependent fashion in pregnant sheep. The response of the HPA-axis to repeated alcohol exposure throughout gestation remained unchanged. Alcohol exposure did not affect the release of thyroid hormones. Thyroid hormone concentrations changed during pregnancy in sheep in a manner similar to changes observed in pregnant women.

Thyrotropin (TSH) is a glycoprotein hormone released from the pituitary gland to promote the synthesis and secretion of thyroid hormone. The existence of well-established peripheral mechanisms for regulation of thyroid hormone delivery to targets has called into question the significance of TSH as a primary regulator of circulating thyroid hormone concentrations in fish. However, relatively little is known about the regulation or action of endogenously secreted teleost TSH, largely due to lack of purified TSH suitable for biological testing and immunoassay development. I developed a red drum in vivo bioassay to aid in the production and purification of recombinant TSH from the red drum, a perciform fish demonstrating dynamic daily thyroxine (T4) cycles hypothesized to be driven by TSH. Exogenous bovine TSH injection resulted in a time and dose-dependent increase in circulating TSH and T4 in red drum. However, the sensitivity of the red drum thyroid gland to stimulation by bovine TSH was lost during growth under controlled laboratory conditions, even when circulating levels of exogenously-administered mammalian TSH remained elevated. The insensitivity of the thyroid was not due to prior TSH injection or feed source. Because insensitivity of the Thyrotropin (TSH) is a glycoprotein hormone released from the pituitary gland to promote the synthesis and secretion of thyroid hormone. The existence of well-established peripheral mechanisms for regulation of thyroid hormone delivery to targets has called into question the significance of TSH as a primary regulator of circulating thyroid hormone concentrations in fish. However, relatively little is known about the regulation or action of endogenously secreted teleost TSH, largely due to lack of purified TSH suitable for biological testing and immunoassay development. I developed a red drum in vivo bioassay to aid in the production and purification of recombinant TSH from the red drum, a perciform fish demonstrating dynamic daily thyroxine (T4) cycles hypothesized to be driven by TSH. Exogenous bovine TSH injection resulted in a time and dose-dependent increase in circulating TSH and T4 in red drum. However, the sensitivity of the red drum thyroid gland to stimulation by bovine TSH was lost during growth under controlled laboratory conditions, even when circulating levels of exogenously-administered mammalian TSH remained elevated. The insensitivity of the thyroid was not due to prior TSH injection or feed source. Because insensitivity of the red drum thyroid precluded their use as a bioassay species, the plasma TSH and T4 response to exogenous TSH was next characterized in goldfish. The T4 response in goldfish was stable and repeatable, with T4 levels peaking at 5 hours and remaining elevated for more than 11 hours after bovine TSH injection. Plasma TSH peaked from 2-5 hours following TSH injection with more than 90 percent cleared by 11 hours. The goldfish bioassay was further utilized to evaluate the effects of structural modifications on TSH biological activity. Substitution of four positively charged amino acids at the n-recombinant human TSH, had the same effect in goldfish. The heterothyrotropic potency of mammalian follicle stimulating hormone in goldfish was also enhanced by the same amino acid substitutions. Finally, the importance of oligosaccharides to TSH bioactivity was also examined in goldfish. Deglycosylation abolished TSH bioactivity, even when immunoreactivity persisted in circulation. Furthermore, recombinant canine TSH was less potent when produced in cell lines generating insect-type glycosylation than when produced in a cell line capable of mammalian-type glycosylation. These studies utilizing recombinant mammalian demonstrated conservation of mammalian TSH hormone-receptor interactions in goldfish, suggesting TSH function might likewise be conserved. Thus, I have established goldfish as a sensitive and stable bioassay which can now be utilized to monitor the biological activity of teleost TSH expressed in vitro as well as to evaluate how structural modifications of the TSH molecule influence its vivo biological activity.

No description available.

Cave (Petrochelidon fulva) and cliff swallows (Petrochelidon pyrrhonota) were collected along the Rio Grande and evaluated as potential indicators of environmental contamination. The Rio Grande receives toxic substances from agricultural, industrial, municipal, and non-point sources; consequently, high levels of contaminants have been detected in birds, mammals, fishes and sediments. Swallows were obtained from 8 sites between Brownsville and El Paso, as well as from a reference site in Burleson County, 320 miles north of the nearest site of the Rio Grande. Blood samples were analyzed by flow cytometry, a technique that allows the detection of DNA damage in blood and other tissues. Plasma samples were analyzed for thyroid hormones using a radioimmunoassay technique. Organochlorines and trace metal analysis was limited to a few samples. DDE and PCB levels were below levels known to cause reduced hatching, embryo mortality, and deformities, Hg, Pb, and As were below detection, and Se, Ni and Cr concentrations were lower than levels known to cause harm in birds. Neither species showed sex-related differences in chromosome damage. Cave swallows from the Del Rio area had the highest levels of DNA variation, which may be indicative of DNA damage, possibly from PAHs exposure. Previous studies indicate that sediment samples from tributaries near Del Rio have high levels of chromium compared to other sites along the Rio Grande. A significant increase in DNA variation between sampling years was detected in cave swallows from Llano Grande Lake. Wildlife samples collected from Llano Grande Lake have recorded high levels of DDE and PCBs; in addition, this urban/agricultural contaminant sink appears to be affected by PAH exposure. T3 levels were below the detection limit of the radioimmunoassay. There were no gender related differences in T4 levels in cave swallows. Cave swallows sampled from Laredo had significantly higher T4 levels than those from birds at other sites during 1999. It was not possible to determine thyroid hormone disruption in plasma samples. Thyroid hormone and flow cytometry data were useful in establishing baseline data. Areas of concern based on genotoxic data include Llano Grande Lake, Del Rio, and El Paso.