Polybrominated dibenzo-p-dioxins (PBDD) and dibenzofurans (PBDF) are a group of compounds of emerging interest as potential environmental stressors. Their structures as well as toxic responses are similar to the highly characterized toxicants polychlorinated dibenzo-p-dioxins. High levels of PBDDs have been found in algae, shellfish, and fish, also from remote areas in theBaltic Sea. This thesis presents studies on PBDD behavior in fish and offspring, and natural formation of PBDDs from naturally abundant phenolic precursors. The uptake, elimination, and maternal transfer of mono- to tetraBDD/Fs were investigated in an exposure study reported in Paper I. The effects of PBDDs in fish were examined in a dose-response study (Paper II). It was shown that fish can assimilate PBDD/Fs from their feed, although non-laterally substituted congeners were rapidly eliminated. Laterally substituted congeners were retained as was congeners without vicinal hydrogens to some extent. PBDD/Fs were transferred to eggs, and congeners that were rapidly eliminated in fish showed a higher transfer ratio to eggs. Exposure to the laterally substituted 2,3,7,8-TeBDD had significant effects on the health, gene expression and several reproduction end-points of zebrafish, even at the lowest dose applied. The geographical and temporal variations of PBDD in biota samples from the Baltic Seasuggest biogenic rather than anthropogenic origin. In Paper III, bromoperoxidase-mediated coupling of 2,4,6-tribromophenol yielded several PBDD congeners, some formed after rearrangement. The overall yield was low, but significantly higher at low temperature, and the product profile obtained was similar to congener profiles found in biota from the Swedish West Coast. In Paper IV, photo­chemi­cally induced cyclization of hydroxylated polybrominated diphenyl ethers under natural conditions produced PBDDs at percentage yield. Rearranged products were not detected, and some abundant congeners do not seem to be formed this way. However, the product profile obtained was similar to congener profiles found in biota from the Baltic Proper. Since the PBDD congeners found in biota have a high turn-over in fish, the exposure must be high and continuous to yield the PBDD levels measured in wild fish. Thus, PBDDs must presumably be formed by common precursors in general processes, such as via enzymatic oxidations, UV-initiated reactions or a combination of both. The presented pathways for formation of PBDDs are both likely sensitive to changes in climatic conditions.

Os retardantes de chama bromados são substâncias utilizadas em bens de consumo para aumentar sua resistência ao fogo e/ou altas temperaturas. Para este fim os Éteres Difenílicos Polibromados (PBDEs do inglês polybrominated diphenyl ether) representam a classe mais utilizada tendo em vista sua eficiência no controle da propagação da chama e baixo custo. Estes compostos são considerados persistentes, bioacumuláveis, podem ser transportados para longas distâncias e apresentam toxicidade podendo causar desregulação endócrina, entretanto os mecanismos de toxicidade ainda não foram bem estabelecidos. Desta forma, o presente projeto utilizou linhagens celulares de Hepatoblastoma Humano (HepG2), HeLa, Hepatócitos e linfócitos humanos a fim de elucidar seus mecanismos de toxicidade. Os resultados significativos demonstram a capacidade destes compostos em induzir dano primário no DNA (0,5 ?mol/L para o BDE-153 e 5 ?mol/L para o BDE-100) monitorado pelo teste do cometa, que não foi reparado após 24 horas de exposição. No entanto, não se observou um aumento de micronúcleos em HepG2 e linfócitos após exposição aos congêneres (0,1 - 25 ?mol/L) nem mesmo mutagenicidade no ensaio de Salmonella typhimurium. Contudo, os compostos apresentam capacidade de diminuir a redução do brometo de 3-(4,5 dimetiltiazol-2il)-2,5 difenil tetrazólio (MTT), proliferação e interferem no ciclo celular nos cultivos celulares avaliados. Estes efeitos de citotoxicidade estão relacionados com a disfunção mitocondrial, uma vez que ambos PBDEs geram dissipação do potencial de membrana mitocondrial, formação e acúmulo de espécies reativas, culminando em morte celular apoptótica, demonstrada pela manutenção da fosfatidil serina na face externa da membrana celular, pela condensação e fragmentação nuclear, presença de fatores pró-apoptóticos no citosol da célula, tais como citocromo C e AIF além da ativação de caspases 3 e 9. Estes dados corroboram com o fato de não ter liberação de lactato desidrogenase intracelular, excluindo a morte celular por necrose. E por fim, foi possível observar que a exposição aos compostos ativa o processo autofágico, a princípio como um mecanismo de citoproteção observado pela conversão de LC3I em LC3II e acúmulo de p62 (marcadores autofágicos) além de marcações imunicitoquímicas para LC3II e co-localização de lisossomos no padrão pontuado, indicanto acúmulos da proteína LC3 e lisossomos, formando os autofagossomos. Em conjunto nossos resultados apresentam a capacidade de induzir instabilidade genômica e citotoxicidade desta classe de compostos, reforçando a idéia de que os PBDEs representam risco à população exposta / The brominated flame retardants are substances used in consumer goods to increase its fire resistance and/or high temperatures. Due to, the polybrominated diphenyl ethers (Polybrominated diphenyl ether) are the most commonly used class in view of its efficiency in controlling the spread of flame and low cost. These compounds are considered persistent, bioaccumulative, can be transported over long distances and have toxicity. However the toxic mechanisms of action have not been well established. Thus, this project held cytotoxic, genotoxic and mutagenic assays in HepG2, HeLa, hepatocytes and human lymphocytes cells in order to elucidate the mechanisms of toxicity. The results demonstrate the ability of these compounds to induce primary DNA damage (0.5 ?M for BDE-153 and 5 ?M for BDE-100) monitored by the comet assay, it was not repaired after 24 hours of exposure. However, there was not observed nether increase in micronuclei in HepG2 cells and lymphocytes after exposure to the congeners (0.1 - 25 ?M) even in the Salmonella typhimurium mutagenicity assay. However, the compounds show the ability to reduce MTT reduction, proliferation, and interfere with cell cycle evaluated in cell cultures. These cytotoxic effects are related to mitochondrial dysfunction, since both PBDE generate dissipation of the mitochondrial membrane potential, accumulation of reactive oxygen species, resulting in apoptotic cell death, demonstrated by the maintenance of serine phosphatidyl on the external surface of the cell membrane, by condensation and nuclear fragmentation, the presence of pro-apoptotic factors in the cytosol of the cell, such as cytochrome c and AIF plus activating caspase 3 and 9. These data corroborate the fact of not having to intracellular lactate dehydrogenase release, excluding death cell necrosis. Finally, it was observed that exposure to the active compounds the autophagic process, at first as a cytoprotective mechanism observed by LC3I conversion in LC3II and accumulation of p62 (autophagic markers) plus imunicitoquímicas markings for LC3II and co-location lysosomes in dotted pattern, indicanto accumulations of LC3 protein and lysosomes, forming autophagosomes. Together our results show the ability to induce genomic instability and cytotoxicity of this class of compounds, reinforcing the idea that PBDEs pose a risk to the exposed population

Decabromodiphenylether (deca-BDE) and triclosan (2,4,4'-trichloro-2'-hydroxydiphenylether) are used in consumer products as flame retardant and bactericide, respectively. Dermal contact is a major human exposure pathway. Deca-BDE and triclosan are known to be photolytically degraded to compounds like lower-BDEs and dioxins. My hypothesis is that photolysis of deca-BDE and triclosan generates free radicals and degradation products which cause toxic effects including cytotoxicity, growth inhibition, oxidative stress and genotoxicity in skin. To test this hypothesis radical formation and photolytic products of deca-BDE and toxic effects of deca-BDE and triclosan alone/with UV-exposure were determined using immortal human keratinocytes (HaCaT) and primary human skin fibroblasts (HSF). My electron paramagnetic resonance and GC-MS studies indicate that deca-BDE is photoreactive and UV irradiation of deca-BDE in organic solvents generates free radicals and lower-BDEs. The free radical formation is wavelength-dependent and positively related to the irradiation time and deca-BDE concentration. In structure-activity relationship studies with deca-BDE, octa-BDE, PBB 209, PCB 209 and diphenyl ether, the presence of halogen atoms (Br > Cl), and/or an ether bond enhance free radical formation. Debromination and hydrogen abstraction from the solvents are the mechanism of radical formation with deca-BDE, which raises concerns about possible toxic effects in UV-exposed skin. In cell culture experiments high levels of triclosan plus UV irradiation and repetitive deca-BDE and UV exposures caused synergistic cytotoxicity in HaCaT. However, neither triclosan nor deca-BDE can be regarded as a phototoxicant following the OECD test and evaluation guidelines. In HSF, no synergistic cytotoxicity was observed, although HSF were more sensitive to deca-BDE and triclosan alone than HaCaT. Contrary to expectations, the photodegradation products of triclosan were less toxic than triclosan itself to HaCaT. However, UV irradiation of triclosan-exposed cells produced a dose dependent increase in intracellular oxidative stress (dichlorofluorescein formation). Comet experiments did not show consistent results of genotoxicity in HaCaT. Overall, deca-BDE and triclosan had no or weak phototoxic potential in cells with the experimental conditions employed. To my knowledge, my research is the first prove of free radical formation during UV irradiation of deca-BDE and the first investigation of phototoxicity of deca-BDE and triclosan in human skin cells.

<p>The dietary intake of polybrominated diphenyl ethers (PBDEs) and hexabromocyclododecane (HBCD) have been estimated for Swedish children. A dietary survey performed in 2003, including 4, 8-9 and 11-12 year olds, and concentrations in individual food items were combined. The food included in the study was mainly of animal origin, consisting of fish and shellfish, dairy products, meat products, eggs, animal and vegetable fats and fats from miscellaneous food products. The medium-bound intake of PBDEs (9 congeners) were estimated to 23.0 ng/day, 30.9 ng/day and 27.7 ng/day for 4, 8-9 and 11-12 years olds respectively. The corresponding estimations for HBCD were 7.94 ng/day 10.7 ng/day and 9.46 ng/day for 4, 8-9 and 11-12 years olds respectively. These results show a higher daily intake for 8-9 year olds compared with the other age groups. However, when estimating the daily intake per kg bw, the intake decreases with age. BDE-47 contributed the most to the total intake of PBDEs, with approximately 40%. The food group contributing the most to the intake of PBDEs and HBCD was fish and shellfish, of which non-Baltic fatty fish was the largest contributor. There were no considerable differences between boys and girls in any of the aspects examined. The result from this study show a lower intake of PBDEs and HBCD in Swedish children compared with children in other studies made in Europe and the United States.</p> / <p>Bromerade flamskyddsmedel används för att skydda brännbara material från att fatta eld, till exempel skyddas textilier och plaster i bland annat elektronik, fordon och möbler. Två typer av bromerade flamskyddsmedel är polybromerade difenyletrar (PBDE) och hexabromocyklododekan (HBCD). Dessa är additiva flamskyddsmedel och blandas i materialet som ska skyddas men binder inte in i produkten och kan därför lätt läcka ut i miljön, vilket också har skett. Halter har påträffats i miljön och i biota långt från plaster där ämnena produceras eller används.</p><p>PBDE och HBCD har visats ha hormonstörande och neurotoxiska effekter i studier på råtta och mus. Thyroxinnivåerna sjunker vid exponering av PBDE och HBCD, vilket skulle kunna leda till sköldkörtelproblem och störd utveckling av bland annat hjärnan om exponering sker perinatalt. De neurotoxiska effekterna inkluderar inlärnings- och minnessvårigheter och ett förändrat beteende med hyper- och hypoaktivitet som följd.</p><p>Human exponering för PBDE och HBCD sker främst via födan och speciellt via animaliska produkter då dessa ämnen är lipofila, bioackumulerande och ofta biomagnifierande vilket gör att de påträffas i högre koncentrationer högre upp i trofinivåerna. Studier från bland annat Sverige och Finland visar att fisk och skaldjur är den största källan till intag av PBDE.</p><p>De flesta intagsberäkningar av PBDE och HBCD baseras på livsmedelskonsumtionen hos vuxna och visar följaktligen endast hur intaget ser ut för den delen av populationen. För barn, som är en av de känsligaste grupperna i populationen, finns inte många studier att tillgå, varken från Sverige eller andra delar av världen. I den här studien har därför intaget av PBDE (summan av 9 kongener) och HBCD beräknats för barn i Sverige.</p><p>I en rikstäckande kostundersökning utförd 2003 deltog barn i åldrarna 4, 8-9 och 11-12 år. De fick i en matdagbok ange sin konsumtion under fyra på varandra följande dagar. Data från denna undersökning kombinerades sedan med haltdata från olika livsmedel för att räkna ut intaget av PBDE och HBCD på individbasis. Undersökningen innefattade främst animaliska livsmedel och innehöll därför fisk och skaldjur, mejeriprodukter, köttprodukter, ägg, animaliskt och vegetabiliskt fett och fett från övriga livsmedel.</p><p>Resultaten visar att födointaget av PBDE var 23,0 ng/dag, 30,9 ng/dag och 27,7 ng/dag för 4, 8-9 respektive 11-12 åringar. Intaget av HBCD beräknades till 7,94 ng/dag, 10,7 ng/dag och 9,46 ng/dag för 4, 8-9 respektive 11-12 åringar. Detta visar att 8-9 åringar har det högsta dagliga intaget av PBDE och HBCD. När intaget beräknas på kroppsvikt däremot, har de yngsta barnen det högsta intaget som sedan sjunker med åldern. Fisk och skaldjur var den största källan till intaget av PBDE och HBCD, trots att konsumtionen av dessa livsmedel var relativt lågt. Det fanns ingen större skillnad mellan pojkar och flickor, varken i intag av PBDE eller av HBCD. Jämfört med de få studier som gjorts i andra länder, är det tydligt att svenska barn har ett lägre intag av PBDE och HBCD.</p><p>Undersökningen tyder också på att intaget av PBDE och HBCD hos svenska barn, utifrån de kunskaper vi har idag, inte utgör någon risk med avseende på de effekter av PBDE och HBCD som påträffats i toxikologiska studier. Däremot är barn i ett känsligt skede i livet och upprepad exponering samt exponering för flera miljögifter samtidigt skulle kunna påverka deras utveckling negativt.</p>

<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.

Persistent organic pollutants (POPs) are toxic chemicals that can be found in various matrices in all corners of the planet, including remote areas such as the Arctic.  Several POPs are known and monitored but given the abundance of new chemicals in commerce about which little is known, chemicals that may be new POPs are constantly being screened for. The use of flame retardants, particularly brominated flame retardants (BFRs), has been increasing for decades. PBDEs and HBCDDs are two types of BFRs that have historically been used in large volumes but recently faced legislative restrictions. However, in order to meet fire safety standards, these BFRs have been replaced by a variety of emerging flame retardants (EFRs) about which little is known especially concerning their toxicity, production volumes, and environmental behavior. The main purpose of this thesis was to investigate the occurrence and fate in indoor and outdoor environments of several EFRs and compare them with PBDEs, HBCDDs, and legacy POPs. Several indoor environments in the city of Stockholm, Sweden were sampled for dust, indoor air, and ventilation system air (Paper II).  Results from these samples revealed a number of EFRs that humans are exposed to and that are emitted from buildings through ventilation systems. These included DDC-CO, DBE-DBCH, PBT, HBB, EHTBB, and BEH-TEBP. PBDE levels seem to be declining compared to previous studies in Stockholm.  Outdoor air and soil were sampled across transects of Stockholm (Paper II) and Birmingham, United Kingdom (Paper III).  Results from these samples showed the presence of many of the same EFRs in the outdoor environment that were found in indoor environments.  Urban pulses in air were discovered for PBDEs in both cities and for some EFRs in Stockholm, indicating that the cities are sources of EFRs to the outdoor environment.  Atmospheric deposition samples were taken at two sites in northern Sweden (Paper I).  Three EFRs (DDC-CO, DBE-DBCH, and BTBPE) and two current-use pesticides (trifluralin and chlorothalonil) were identified, indicating these compounds’ potential for long range transport and global contamination.  Other legacy POPs such as HCH, PCBs, and PBDEs were measured in the deposition samples as well.  The bulk of deposition was comprised of HCH and PCBs with only minor contributions from PBDEs, chlordanes, and emerging compounds.  Finally, passive and active air sampling methods were compared for BFRs in offices in Beijing, China.  Some EFRs were identified in indoor air from China; however, BDE-209 was the most predominant compound found (Paper IV).  Air samples collected with passive samplers generally had measured FR concentrations within a factor of 2-3 of those collected with active samplers. The use of a GFF in the passive samplers resulted in concentrations of particle-bound contaminants such as BDE-209 that were more comparable to those in active samples. The positioning of the PUF in the passive samplers affected the sampling rates for gaseous compounds and particle retention on PUFs was shown to be a large source of uncertainty in passive sampling. / <p>At the time of the doctoral defense, the following papers were unpublished and had a status as follows: Paper 3: Manuscript. Paper 4: Manuscript.</p><p> </p>

Polybrominated diphenyl ethers (PBDEs) are synthetic chemicals that are added to a variety of consumer products as flame-retardants. The ubiquitous nature and endocrine disrupting properties of PBDEs are a public concern. A pilot study was performed to investigate whether in utero PBDE exposure, as measured in maternal hair, is associated with genitourinary tract malformations in male infants. In addition, we compared PBDE levels in maternal and infant hair and used segmental analysis to investigate how PBDEs varied along the shaft. Preliminary results suggest a trend toward an elevated PBDE body burden in mothers whose infants were born with genitourinary tract malformations; this was significant for some PBDEs. The sum of PBDEs (ΣPBDEs) in maternal hair did not correlate with infant hair levels; children had significantly greater levels. A significant increase in the ΣPBDEs was observed in distal hair suggesting hair PBDEs may be reflective of both internal and external exposure.

Os retardantes de chama bromados são substâncias utilizadas em bens de consumo para aumentar sua resistência ao fogo e/ou altas temperaturas. Para este fim os Éteres Difenílicos Polibromados (PBDEs do inglês polybrominated diphenyl ether) representam a classe mais utilizada tendo em vista sua eficiência no controle da propagação da chama e baixo custo. Estes compostos são considerados persistentes, bioacumuláveis, podem ser transportados para longas distâncias e apresentam toxicidade podendo causar desregulação endócrina, entretanto os mecanismos de toxicidade ainda não foram bem estabelecidos. Desta forma, o presente projeto utilizou linhagens celulares de Hepatoblastoma Humano (HepG2), HeLa, Hepatócitos e linfócitos humanos a fim de elucidar seus mecanismos de toxicidade. Os resultados significativos demonstram a capacidade destes compostos em induzir dano primário no DNA (0,5 ?mol/L para o BDE-153 e 5 ?mol/L para o BDE-100) monitorado pelo teste do cometa, que não foi reparado após 24 horas de exposição. No entanto, não se observou um aumento de micronúcleos em HepG2 e linfócitos após exposição aos congêneres (0,1 - 25 ?mol/L) nem mesmo mutagenicidade no ensaio de Salmonella typhimurium. Contudo, os compostos apresentam capacidade de diminuir a redução do brometo de 3-(4,5 dimetiltiazol-2il)-2,5 difenil tetrazólio (MTT), proliferação e interferem no ciclo celular nos cultivos celulares avaliados. Estes efeitos de citotoxicidade estão relacionados com a disfunção mitocondrial, uma vez que ambos PBDEs geram dissipação do potencial de membrana mitocondrial, formação e acúmulo de espécies reativas, culminando em morte celular apoptótica, demonstrada pela manutenção da fosfatidil serina na face externa da membrana celular, pela condensação e fragmentação nuclear, presença de fatores pró-apoptóticos no citosol da célula, tais como citocromo C e AIF além da ativação de caspases 3 e 9. Estes dados corroboram com o fato de não ter liberação de lactato desidrogenase intracelular, excluindo a morte celular por necrose. E por fim, foi possível observar que a exposição aos compostos ativa o processo autofágico, a princípio como um mecanismo de citoproteção observado pela conversão de LC3I em LC3II e acúmulo de p62 (marcadores autofágicos) além de marcações imunicitoquímicas para LC3II e co-localização de lisossomos no padrão pontuado, indicanto acúmulos da proteína LC3 e lisossomos, formando os autofagossomos. Em conjunto nossos resultados apresentam a capacidade de induzir instabilidade genômica e citotoxicidade desta classe de compostos, reforçando a idéia de que os PBDEs representam risco à população exposta / The brominated flame retardants are substances used in consumer goods to increase its fire resistance and/or high temperatures. Due to, the polybrominated diphenyl ethers (Polybrominated diphenyl ether) are the most commonly used class in view of its efficiency in controlling the spread of flame and low cost. These compounds are considered persistent, bioaccumulative, can be transported over long distances and have toxicity. However the toxic mechanisms of action have not been well established. Thus, this project held cytotoxic, genotoxic and mutagenic assays in HepG2, HeLa, hepatocytes and human lymphocytes cells in order to elucidate the mechanisms of toxicity. The results demonstrate the ability of these compounds to induce primary DNA damage (0.5 ?M for BDE-153 and 5 ?M for BDE-100) monitored by the comet assay, it was not repaired after 24 hours of exposure. However, there was not observed nether increase in micronuclei in HepG2 cells and lymphocytes after exposure to the congeners (0.1 - 25 ?M) even in the Salmonella typhimurium mutagenicity assay. However, the compounds show the ability to reduce MTT reduction, proliferation, and interfere with cell cycle evaluated in cell cultures. These cytotoxic effects are related to mitochondrial dysfunction, since both PBDE generate dissipation of the mitochondrial membrane potential, accumulation of reactive oxygen species, resulting in apoptotic cell death, demonstrated by the maintenance of serine phosphatidyl on the external surface of the cell membrane, by condensation and nuclear fragmentation, the presence of pro-apoptotic factors in the cytosol of the cell, such as cytochrome c and AIF plus activating caspase 3 and 9. These data corroborate the fact of not having to intracellular lactate dehydrogenase release, excluding death cell necrosis. Finally, it was observed that exposure to the active compounds the autophagic process, at first as a cytoprotective mechanism observed by LC3I conversion in LC3II and accumulation of p62 (autophagic markers) plus imunicitoquímicas markings for LC3II and co-location lysosomes in dotted pattern, indicanto accumulations of LC3 protein and lysosomes, forming autophagosomes. Together our results show the ability to induce genomic instability and cytotoxicity of this class of compounds, reinforcing the idea that PBDEs pose a risk to the exposed population

Polybrominated diphenyl ethers belong to group of brominated flame retardants. Important property of these substances is their ability to reduce flammability or to prevent ignition of many products of daily use, such us televisions, carpets, mattresses and many others. Polybrominated diphenyl ethers however are characterized by high persistence and lipophility, leading to their accumulation in the environment. In recent years, concerns about the effects of organic halogen compounds on human health, suggesting their inclusion in the list of persistent organic pollutants in 2009. These contaminants are capable of long-range transport and accumulation in the environment. Therefore, the presence of polybrominated diphenyl ethers is systematically observed in the abiotic and biotic components of the environment worldwide. Their presence has been demonstrated in areas that are clearly very distant from sources of contamination. This thesis is focused on the use of gas chromatography to assess the level of contamination of selected components of the environment, especially of soil. For these purposes was used method of gas chromatography with electron capture detection mass spectrometry.