A novel method for determination of tetrabromobisphenol-A (TBBPA), was developed using gas chromatography-negative ion chemical ionization-mass spectrom- etry (GC-NCI-MS). Samples of municipal wastewater treatment plant (WWTP) influent were analyzed for TBBPA. Levels ranged from 1 to 41 ng/L, with an average of 20 ± 14 ng/L. Matrix effects were shown to be 30 ± 17 % in the influent and -30 ± 11 % in membrane permeate. The method limit of quantitation was 0.1 ng/L TBBPA. Sorption of TBBPA to fresh mixed-liquor suspended solids (MLSS) from a membrane bioreactor (MBR) were studied. In a kinetic study, sorption was found to be essentially complete after 12 hours of exposure to MLSS. Log Koc and log Kd were measured at 4.7 ± 0.8 and 1.9 ± 0.8 respectively (n = 22). These values were much higher than modelled estimates based on Kow (p ≥ 0.05), and higher than modelled estimates based on Kow and pKa (p ≥ 0.05). Data was successfully modelled using the Freundlich isotherm, having a Kf value of 8.5 and an n value of 1.7. TBBPA adsorbed to borosilicate glassware, with a wall-loss coefficient (Kw) of 0.15 ± 0.1 (n ≥ 3). TBBPA levels in WWTP influent varied from 13 to 29 ng/L while effluent concentrations varied from 0 to 2.2 ng/L over the same period. Three pilot-scale membrane bioreactors (MBRs) removed less TBBPA during the same time period, though MBR removal was also significant (p ≥ 0.05). Increasing MBR sludge residence time (SRT) increased removal at the 86 % confidence interval (p = 0.14). A nitrifying MABR was shown to remove TBBPA significantly when spiked with ammonia and TBBPA (p ≥ 0.05), showing that nitrifying bacteria can degrade TBBPA. An MABR hollow fibre was found to adsorb TBBPA. Various soluble microbial products (SMP) were studied from MBRs fed munici- pal influent. Using current measurement practices, SMP were shown to be sensitive to matrix effects. Use of the standard addition technique (SA) can compensate for this. Measurements using SA showed SMP degrades rapidly during storage in the fridge and due to freezing. SA was also used to compare commonly used SMP extraction techniques, and showed that extraction method influences recovery.

Summary Polybrominated diphenyl ethers (PBDEs) are a class of brominated flame retardants. The addition of these chemicals to electrical and electronic equipment, building materials, carpet and textiles reduces flammability and therefore harm and destruction caused by unwanted fire. These chemicals are now internationally ubiquitous in the environment and humans because of their increased usage and physical and chemical properties of persistence and lipophilicity. Although Australian data on both the concentrations and the sources and exposure pathways was limited, a preliminary study of PBDEs in 10 pools of human blood serum revealed that concentrations of PBDEs in Australia were comparatively higher than most countries with the exception of Canada and the USA. The aim of this project was to determine the concentrations of PBDEs in the Australian population and to examine the possible sources and pathways of exposure in humans. Experimental evaluation of PBDE exposure matrices included samples of: sediment (n=46), air (n=19), dust (n=19), surface wipes (n=10) and human milk (157 samples combined into 17 pools, n=10 individual samples); and the general population using human blood serum (10552 samples combined into 169 pools). With accumulating evidence regarding age differences in PBDE concentrations, the scope of this project was broadened to include a focus on infants and young children. This study found that PBDE contamination was widespread in the Australian environment and human population. In sediment, PBDEs were relatively low at the majority of sites with mean ± standard deviation and median ΣPBDE concentrations across all sites of 4707 ± 12580 and 305 pg g-1 dw, respectively. There were elevated concentrations found downstream of sewerage treatment plants; in areas dominated by industrial and urban land-use types; and in estuarine compared to freshwater environments. PBDEs were detected in air, dust and surface wipes. Concentrations on the whole were found to be higher indoors compared to outdoors and in offices compared to homes. ΣPBDE concentrations ranged from 0.5 -179 pg/m3 for homes and 15 - 487 pg/m3 for offices and at the two outdoor sites the concentrations were 1.7 and 6.8 pg/m3. PBDEs were detected on 9 out of 10 surfaces (e.g. television, refrigerator, DVD player) sampled and ranged from non-detectable to 5985 pg/cm2 while in dust, ΣPBDEs ranged from 87 - 733 ng/g dust in homes and 583 - 3070 ng/g dust in offices. PBDEs were detected in all individual and pooled samples of human milk and blood serum and the ΣPBDE and BDE-47 concentrations ranged from 5.5 to 103 and 0.6 to 55 ng/g lipid, respectively. There were no regional differences in concentrations in human milk or blood serum and in general PBDE concentrations were higher in males than in females. Although no temporal trend was apparent in samples of human milk or blood serum collected between 2002 and 2008, the ban on penta- and octa-BDE commercial products in several countries has only been in place since 2004. Hence, effects of the ban may not be reflected in human body burden for several years. The concentrations of PBDEs were found to be highest in young children aged 2 – 5 years of age where concentrations were up to 10 times greater than those detected in adults. Congener profiles for sediment, air, dust and surface wipes were mostly dominated by BDE-209. In human milk and serum, BDE-47 was dominant while BDE-209 contributed only 3% in human milk and was not determined in serum. Concentrations of PBDEs found in Australian human and environmental samples were lower than those reported from North America but higher than those reported from Europe and Asia. The results of modeling and the assessment of matched samples of human milk, indoor air and dust showed that body burden could be partly explained by exposure via food, air, dust and human milk as well as clearance (half-life) data. However, the higher than expected concentrations in young children indicated that there are likely to be missing sources and exposure pathways and/ or the clearance data is inaccurate. The results of this thesis provide baseline data on PBDE concentrations in Australia and will prove important for long term monitoring of the effect of changes in usage rates of these chemicals. It is important to understand the specific sources and exposure pathways of PBDEs in infants and young children in order to identify intervention methods whereby exposure to this vulnerable population can be reduced. In terms of the future use of PBDEs or other flame retardant chemicals, it is important that the risk-benefit ratio is regulated so that the minimization of human exposure and potential associated negative health effects is balanced with the reduction of harm caused by fire.

Poly Brominated Diphenyl Ethers (PBDEs) are known flame retardants with highly persistent and lipophilic in nature. The continued usage of PBDE in various products amplifies the human burden of PBDEs. It is therefore, important to study the potential toxicological and/or biological effects of PBDE exposure in human. In this study we investigated the mode of action of PBDE induced toxicity in human liver by exposing human hepatocarcinoma cells in a time (24-72h) and dose (0-100μM) dependent manner. The highest test dose caused an inhibition in cell viability up to 50% after 72h, whereas lower doses (<50μM) showed slight increase in cell viability. Likewise, higher doses caused significant accumulation of intracellular ROS over time. Further, increase in caspase-3 enzyme levels and DNA fragmentation showed that, lower brominated PBDEs induce liver toxicity through accumulation of toxic metabolites and reactive oxygen species over time leading to caspase-mediated apoptotic cell death.

In the recent years, many research articles focused on endocrine disrupting compounds in the environment. Some of these compounds are listed in a group named brominated flame retardants. However, only few articles investigated endocrine activity of several "new" brominated flame retardants. These chemicals such as 1,2-bis(2,4,6-tribromophenoxy)ethane (BTBPE) or bis(2-ethylhexyl) tetrabromophthalate (TBPH) are newly used due to ban of some previously most produced brominated flame retardant mixes. In this study, we used two recombinant yeast screens to measure estrogenic, androgenic, antiestrognic and antiandrogenic activities of some alternative brominated flame retardants. We also used ligninolytic fungi to investigate biodegradation of these compounds. Our results suggest, that 2,4,6-tribromophenol (TBP) may be a new environmental endocrine disruptor. This substance showed antiestrogenic and antiandrogenic activity in our tests. 1,2-bis(2,4,6- tribromophenoxy)ethane (BTBPE) had certain antagonistic activity too. In the biodegradation experiment, only three compounds showed significant degradation during the test period. No biodegradation have been observed for other compounds. In this study, we applied gas chromatography with mass spectrometry to analyze these "new" flame retardants. Method for gas...

No description available.

<p>Polybrominated diphenyl ethers (PBDEs) are a class of brominated flame retardant chemicals that are added to plastics, electronic components, furniture foam, and textiles to reduce their combustibility. Of the three commercial mixtures historically marketed, only DecaBDE, which is constituted almost entirely (~97%) of the fully brominated congener decabromodiphenyl ether (BDE-209), continues to be used in the U.S. today. While decaBDE is scheduled for phase-out in the U.S. at the end of 2013, exposures to BDE-209 and other PBDEs will continue into the foreseeable future as products that contain them continue to be used, recycled, and discarded. In addition, decaBDE use continues to be largely unrestricted across Asia, although restricted from use in electronic equipment in Europe. </p><p>Despite limits placed on PBDE uses, they are ubiquitous contaminants detected worldwide in humans and wildlife. Major health effect concerns for PBDEs come largely from evidence in laboratory rodents demonstrating neurotoxicity, reproductive and developmental impairments, and thyroid disruption. The potential for PBDEs, particularly BDE-209, to disrupt thyroid regulation and elicit other toxic outcomes in fish is less clear. Thus, the overall objective of this thesis research was to answer questions concerning how fish, as important indicators of overall environmental health, are metabolizing PBDEs and whether and how PBDEs are disrupting thyroid hormone regulation. The central hypothesis was that PBDE metabolism in fish is mediated by iodothyronine deiodinase (dio) enzymes, which are responsible for activating and inactivating thyroid hormones, and that PBDE exposures are causing thyroid system dysfunction across fish life stages. </p><p>Under the first research aim, in vitro experiments conducted in liver tissues isolated from common carp (Cyprinus carpio) suggested a role for dio enzymes in catalyzing the reductive debromination of PBDEs. Carp liver microsomes efficiently debrominated BDE-99 to BDE-47, and enzymes catalyzing this reaction were associated predominantly with the endoplasmic reticulum (i.e., microsomal fraction) where dio enzymes are located. Competitive substrate experiments in carp liver microsomes also demonstrated that rates of BDE-99 debromination to BDE-47 were significantly inhibited upon challenges with 3,3',5'-triiodothyronine (rT3) and thyroxine (T4). This finding supported the hypothesis that enzymes involved in the metabolism of PBDEs may have high affinities for thyroid hormones. Indeed, experiments to determine apparent enzymatic kinetics (apparent Vmax and Km values) of BDE-99 hepatic metabolism suggested that enzymes responsible for the catalytic activity appeared to have a higher affinity for native thyroid hormone than BDE-99. </p><p>The second and third research aims were focused on evaluating BDE-209 accumulation, metabolism, and thyroid toxicity in juvenile and adult life stages of fish using the fathead minnow (Pimephales promelas) as a model. BDE-209 bioaccumulated and was debrominated to several reductive metabolites ranging from penta- to octaBDEs in both juvenile and adult fish exposed to BDE-209. In addition, thyroid hormone regulation in juvenile and adult male fathead minnows was severely disrupted by BDE-209 at low, environmentally relevant exposures. In juvenile minnows, the activity of dio enzymes (T4-outer ring deiodination; T4-ORD and T4-inner ring deiodination; T4-IRD) declined by ~74% upon oral doses of 9.8 ± 0.2 µg/g wet weight (ww) food at 3% body weight (bw)/day for 28 days, compared to controls. Declines in dio activity were accompanied by thyroid follicle hypertrophy indicative of over-stimulation and injury. In addition to thyroid disruption, a distinctive liver phenotype characterized by vacuolated hepatocyte nuclei was measured in ~48% of hepatocytes from treated fish that was not observed in controls. </p><p>Under the third research aim, adult male fathead minnows received dietary treatments of BDE-209 at a low dose (95.3 ± 0.41 ng/g-food at 3% bw/day) and a high dose (10.1 ± 0.10 µg/g-food at 3% bw/day) for 28 days followed by a 14-day depuration period to evaluate recovery. Compared to negative controls, adult male fish exposed orally to BDE-209 at the low dose tested for 28 days experienced a 53% and 46% decline in circulating total T4 and T3, respectively, while fish at the high BDE-209 dose tested had total T4 and T3 deficits of 59% and 62%, respectively. Depressed levels of plasma thyroid hormones were accompanied by a 45-50% decline in the rate of T4-ORD in brains of all treatments by day 14 of the exposure. The decreased T4-ORD continued in the brain at day 28 with a ~65% decline measured at both BDE-209 doses. BDE-209 exposures also caused transient, tissue-specific upregulations of relative mRNA transcripts encoding dio enzymes (dio1, dio2), thyroid hormone receptors (TR&alpha, TR&beta), and thyroid hormone transporters (MCT8, OATP1c1) in the brain and liver in patterns that varied with time and dose, possibly as a compensatory response to hypothyroidism. In addition, thyroid perturbations at the low dose tested generally were equal to those measured at the high dose tested, suggesting non-linear relationships between PBDE exposures and thyroid dysfunction in adult fish. Thus, mechanisms for BDE-209 induced disruption of thyroid regulation can be proposed in adult male minnows that involve altered patterns of thyroid hormone signaling at several important steps in their transport and activation. </p><p>A growing body of evidence describing PBDE toxicity in biota, including data generated here, along with studies showing continued and rising PBDE body burdens, raises concern for human and wildlife health. Long delays in removing PBDEs from the market, their ongoing presence in many products still in use, and their active use outside the U.S. and European Union will leave a lasting legacy of rising contamination unless more concerted regulatory and policy actions are taken to reduce future exposures and harm.</p> / Dissertation

<p>This thesis examines developmental neurotoxic effects of polybrominated diphenyl ethers (PBDEs), PBDE 99, PBDE 153, and the fully brominated PBDE 209, after exposure during the newborn period in rodents.</p><p>Our environment contains vast numbers of contaminants, including the flame retardants, PBDEs. The PBDEs are widely found in the environment and are increasing in human milk. Individuals can be exposed to PBDEs during their whole lifetime, and especially during the lactation period. The neonatal period, coinciding with the lactation period, is characterized in many mammalian species by rapid growth and development of the immature brain. It has been shown that numerous toxicants can induce permanent disorders in brain function when administered to the neonatal mouse during the brain growth spurt (BGS). In mice and rats this period is postnatal, spanning over the first 3-4 weeks of life, while in humans, BGS begins during the third trimester of pregnancy and continues throughout the first two years of life.</p><p>The present studies identified a defined critical period during BGS in mice when the brain is vulnerable to insults of low doses of PBDEs and that it is the presence of PBDEs or their metabolites in the brain during this critical period that is crucial to evoking neurotoxic effects. The effects observed are permanent altered spontaneous behavior, reduced habituation, deficits in learning and memory, and disturbances in the cholinergic system. These effects worsen with age.</p><p>The ability of PBDEs to induce neurotoxic effects does not appear to be gender-, strain- or species-specific, because the neurotoxic effects are induced in rats and male and female mice of different strains.</p><p>The developmental neurotoxic effects of PBDEs are similar to those observed for polychlorinated biphenyls (PCBs) and possible interactive effects of PBDEs and other environmental contaminants are therefore of concern.</p>

This thesis examines developmental neurotoxic effects of polybrominated diphenyl ethers (PBDEs), PBDE 99, PBDE 153, and the fully brominated PBDE 209, after exposure during the newborn period in rodents. Our environment contains vast numbers of contaminants, including the flame retardants, PBDEs. The PBDEs are widely found in the environment and are increasing in human milk. Individuals can be exposed to PBDEs during their whole lifetime, and especially during the lactation period. The neonatal period, coinciding with the lactation period, is characterized in many mammalian species by rapid growth and development of the immature brain. It has been shown that numerous toxicants can induce permanent disorders in brain function when administered to the neonatal mouse during the brain growth spurt (BGS). In mice and rats this period is postnatal, spanning over the first 3-4 weeks of life, while in humans, BGS begins during the third trimester of pregnancy and continues throughout the first two years of life. The present studies identified a defined critical period during BGS in mice when the brain is vulnerable to insults of low doses of PBDEs and that it is the presence of PBDEs or their metabolites in the brain during this critical period that is crucial to evoking neurotoxic effects. The effects observed are permanent altered spontaneous behavior, reduced habituation, deficits in learning and memory, and disturbances in the cholinergic system. These effects worsen with age. The ability of PBDEs to induce neurotoxic effects does not appear to be gender-, strain- or species-specific, because the neurotoxic effects are induced in rats and male and female mice of different strains. The developmental neurotoxic effects of PBDEs are similar to those observed for polychlorinated biphenyls (PCBs) and possible interactive effects of PBDEs and other environmental contaminants are therefore of concern.

Polybrominated diphenyl ethers (PBDEs), flame retardants, have been applied to consumer goods, such as furniture, electrical devices, textiles, and appliances for decades. Due to their physico-chemical properties, PBDEs are semi-volatile and easily leach off the consumer good during aging, stress, or normal wear and tear of the good. Once airborne, they pose an environmental health threat because they can adsorb onto dust particles, soil, or other particulates that can be inhaled, ingested, or come into contact with the dermal layer. Additionally, PBDEs have a molecular structure similar to other persistent organic pollutants, such as polychlorinated biphenyls and polychlorinated dibenzo-p-dioxins and furans. They are a health threat due to their endocrine-disrupting nature by affecting thyroid functioning, fertility, and child development. The purpose of the study is to measure selected PBDEs in a wastewater treatment plant (WWTP) that produces reclaimed water, such that a mass balance can be completed, and to compare this mass balance with theoretically expected concentrations. The mass balance includes the collection of samples from wastewater, sewage sludge, and air at points within the WWTP. The PBDEs examined are BDE-28, 47, 99, 100, 153, 154, and 183. The second part of the study will compare effluent concentrations to reclaimed water concentrations in order to examine the potential exposure (if any) of using reclaimed water. Influent concentration of mean (sum7)PBDE was found to be 49,117 pg/L and effluent concentration was 4,603 pg/L, illustrating a 91% removal rate of PBDEs during the wastewater treatment plant. Sludge samples contained the highest total concentrations of PBDEs with mean (sum7)PBDE ranging from 14.0 to 41.3 ug/kg dry weight. Air samples were highest at the post-aeration (248 pg/m3 mean (sum7)PBDE) step due to the use of highly oxygenated air assisting in the release and volatilization of the PBDEs. Sludge was found to carry the largest mass loading at 14.2 lb/day (sum7)PBDE. Of the total mass loading of PBDEs from the WWTP, sludge is responsible for 86.7%, followed by reclaimed water and effluent (11.7% and 1.6%, respectively). The mass loading from air was negligible with less than 0.01% contribution to the total mass loading. Whereas reclaimed water overall had higher PBDE congener mean concentrations than the effluent, the independent samples t-test found no statistically significant differences between the two groups. The results of this study can be used to improve the wastewater treatment process to reduce the impact of PBDEs being released into the environment by WWTPs, and to educate the public on utilizing reclaimed water in a safe and healthy manner.

Halogenation of poly(isobutylene-co-isoprene) (IIR) increases its reactivity towards sulphur and other nucleophiles. Currently brominated (BIIR) and chlorinated (CIIR) derivatives are commercially available; however, an iodinated derivative has been briefly investigated. The effects of leaving group ability and microstructure on the reactivity of halogenated poly(isobutylene-co-isoprene) were studied to put iodobutyl rubber reactivity into context and to compare existing commercial products to their isomeric derivatives. Polymers containing halomethyl (r-CIIR, r-BIIR, r-IIIR) isomers of butyl rubber were prepared from as-received BIIR to compare the effect of leaving group on thermal stability and reactivity towards nucleophilic substitution. The polymer containing (E,Z)-endo-iodomethyl isomers (r-IIIR) readily underwent nucleophilic substitution at low temperatures; however, it was sensitive towards dehydrohalogenation at temperatures above 65⁰C. At temperatures between 100⁰C and 135⁰C, the bromomethyl derivative (r-BIIR) demonstrated the best balance between reactivity toward nucleophilic substitution and dehydrohalogenation. Exceptional thermal stability at temperatures up to 190⁰C was displayed by the chloromethyl derivative (r-CIIR); however, it was unreactive at low temperatures towards certain nucleophiles. This lack of reactivity shown by r-CIIR was not consistent with all nucleophiles, as reaction dynamics with TBAAc display its variable reactivity towards nucleophilic substitution with results parallel to those of r-BIIR. Exo-methylene allylic halides (Exo-Br, Exo-Cl) and (E,Z)-endo-halomethyl (r-BIIR, r-CIIR) isomers were vulcanized with sulphur to determine the effect of microstructure on reactivity. Results showed a clear effect of microstructure on the ability to cure with sulphur. While the Exo-Cl isomer has no ability to cure, when rearranged to its (E,Z)-endo-chloromethyl isomer curing occurs readily. Both the Exo-Cl and (E,Z)-endo-bromomethyl isomers readily vulcanize in the presence of sulphur, however Exo-Br cures to a greater extent. / Thesis (Master, Chemical Engineering) -- Queen's University, 2011-09-30 12:55:25.665