968 resultados para Triglyceride levels
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Effective collision strengths for electron-impact excitation of the N-like ion NeIV are calculated in the close-coupling approximation using the multichannel R-matrix method. Specific attention is given to the 10 astrophysically important fine-structure forbidden transitions among the 4So, 2Do and 2Po levels in the 2s22p3 ground-state configuration. The expansion of the total wavefunction incorporates the lowest 11 LS eigenstates of NeIV, consisting of eight n = 2 terms with configurations 2s22p3, 2s2p4 and 2p5, together with three n = 3 states of configuration 2s22p23s. We present in graphical form the effective collision strengths obtained by thermally averaging the collision strengths over a Maxwellian distribution of velocities, for all 10 fine-structure transitions, over the range of electron temperatures log T(K) = 3.6 to log T(K) = 6.1 (the range appropriate for astrophysical applications). Comparisons are made with the earlier, less sophisticated close-coupling calculation of Giles, and excellent agreement is found in the limited temperature region where a comparison is possible [log T(K) = 3.7 to log 7(K) = 4.3]. At higher temperatures the present data are the only reliable results currently available.
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The multichannel R-matrix method is used to compute electron impact excitation collision strengths in Ar IV for all fine-structure transitions among the 4S°, 2D° and 2P° levels in the 3s 23p 3 ground configuration. Included in the expansion of the total wavefunction are the lowest 13 LS target eigenstates of Ar iv formed from the 3s 23p 3, 3s3p 4 and 3s 23p 23d configurations. The effective collision strengths, obtained by averaging the electron collision strengths over a Maxwellian distribution of electron velocities, are presented for all 10 fine-structure transitions over a wide range of electron temperatures of astrophysical interest (T e = 2000-100 000 K). Comparisons are made with an earlier 7-state close-coupling calculation by Zeippen, Butler & Le Bourlot, and significant differences are found to occur for many of the forbidden transitions considered, in particular those involving the 4S° ground state, where discrepancies of up to a factor of 3 are found in the low-temperature region. © 1997 RAS.
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Currently, there are no biomarkers which can identify patients with an increased risk of developing urothelial cancer as a result of occupational chemical exposure. The aim of this study was to evaluate the relationships between final diagnosis and 22 biomarkers measured in urine, serum and plasma collected from 156 hematuric patients. Fourteen of the 80 patients (17.5%) with urothelial cancer and 13/76 (17.1%) of the controls were deemed to have a history of chemical exposure. We applied Fisher's exact tests to explore associations between chemical exposure and final diagnosis, and tumor stage and grade, where applicable; ANOVA and t-test to compare age across patients with and without chemical exposure; and Zelen's exact test to evaluate relationships across final diagnosis, chemical exposure and smoking. Following pre-selection of biomarkers using Lasso, we identified biomarkers with differential levels across patients with and without chemical exposure using Welch's t-test. Using a one-sided t-test and considering multiple testing using FDR, we observed that TM levels in urine were significantly higher in samples from patients with a history of chemical exposure regardless of their diagnosis as control or urothelial cancer (one-sided t-test, pUC = 0.014 and pCTL = 0.043); in the presence of dipstick protein and when urinary pH levels ≤ 6 (p = 0.003), but not in the presence of dipstick blood (p = 0.115). Urothelial cancer patients with a history of chemical exposure were significantly younger (64.1 years) than those without chemical exposure (70.2 years) (one-sided t-test p-value = 0.012); and their tumors were higher grade (Fisher's exact test; p = 0.008). There was a strong association between a history of chemical exposure and smoking in urothelial cancer patients (Zelen's exact test; p = 0.025). Elevated urinary thrombomodulin levels could have the potential to identify chemical exposure in hematuric patients at high risk of developing urothelial cancer.
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Os compostos orgânicos de estanho (OTs), de entre os quais se destaca o tributilestanho (TBT), encontram-se amplamente dispersos no meio aquático devido à sua intensa utilização como agente biocida em tintas antivegetativas. Estudos anteriores sobre a poluição por organoestanhos em Portugal demonstraram que estes compostos se encontram presentes não só na linha de costa mas também em zonas da plataforma, sendo as zonas portuárias (onde se incluem portos comerciais, portos de pesca, marinas e estaleiros navais) os principais focos de poluição. A presente tese tem como objectivo investigar o estado actual da poluição por organoestanhos na costa Portuguesa confirmando se os padrões espaciais acima descritos se mantêm, por meio da quantificação de diversos OTs, nomeadamente, butilestanhos, fenilestanhos e octilestanhos. Assim, os níveis destes compostos foram avaliados em populações de Mytilus galloprovincialis e Nassarius reticulatus ao longo da costa continental Portuguesa, com particular incidência na Ria de Aveiro onde se quantificaram os níveis de OTs em mexilhões, gastrópodes e sedimentos, recolhidos numa malha de amostragem mais densa. A distribuição espacial dos organoestanhos foi determinada utilizando o bivalve M. galloprovincialis como espécie bioindicadora. Os níveis totais de estanho (SnT) foram quantificados nos tecidos do mexilhão e relacionados com os níveis totais de OTs nos mesmos tecidos, incluindo monobutilestanho (MBT), dibutilestanho (DBT), tributilestanho (TBT), difenilestanho (DPhT), trifenilestanho (TPhT), monoctilestanho (MOcT) e dioctilestanho (DOct). A contribuição dos OTs para os valores de estanho total (SnT) foi superior nas estações de amostragem localizadas no interior de portos onde atingiram proporções próximas dos 50%. De entre estes, os butilestanhos (BuTs=MBT+DBT+TBT) contribuíram em média com 98.6% para o valor total de OTs, tendo sido detectados em todas as amostras analisadas. Os valores mais elevados foram registados no interior ou na proximidade de portos, corroborando a ideia anterior de que constituem importantes focos de poluição. A variação das concentrações de TBT no mexilhão situou-se entre os 0,9 e 720 ng Sn.g-1 de peso seco (ps). Estes valores são, em 69% das estações amostradas, superiores ao valor do proposto pela OSPAR (4,9 ng TBT-Sn.g-1 ps) para tecidos de mexilhão o que sugere a forte probabilidade de ocorrência de efeitos adversos sobre os ecossistemas. Os níveis de OTs foram também quantificados em tecidos de N. reticulatus recolhidos ao longo da costa em 2008 Os butilestanhos representaram a maioria dos compostos organoestânicos quantificados e os níveis mais elevados foram novamente detectados no interior ou nas imediações de portos. Os valores de TBT nos tecidos deste gastrópode variaram entre 3,5 e 380 ng Sn.g-1 ps, representando uma percentagem média de 50,4% do total de butilestanhos. Simultaneamente, os níveis de imposex foram também avaliados e relacionados com os valores deste composto nos tecidos. As distribuições espaciais de imposex e de TBT seguiram a mesma tendência, sendo que em todos os locais amostrados foram encontradas fêmeas afectadas. Os valores de VDSI (índice da sequência do vaso deferente) variaram entre 0,2 e 4,4. Em 91% dos locais os valores de VDSI foram superiores a 0,3 (definido pela OSPAR como o valor de VDSI em N. reticulatus acima do qual o objectivo de qualidade ecológica não é atingido), confirmando a suspeição da existência de efeitos adversos nos ecossistemas. Em todos os compartimentos analisados na Ria de Aveiro, os butilestanhos foram os principais contribuintes para estanho orgânico total. A utilização do imposex em N. reticulatus como biomarcador da poluição por TBT permitiu determinar um gradiente decrescente desde o interior da Ria (onde se situa a zona portuária) até zonas costeiras adjacentes. O mesmo gradiente foi observado relativamente às concentrações de TBT em tecidos de mexilhão. Para os sedimentos, as concentrações de TBT são bastante variáveis com valores entre 2,7 e 1780 ng Sn.g-1 ps encontrando-se significativamente correlacionadas com o conteúdo em matéria orgânica da amostra. Em todas as amostras analisadas os níveis de TBT são elevados e superiores ao valor inferior (provisório) de EAC (critério de avaliação ambiental) proposto pela OSPAR (0,004 ng TBT-Sn.g-1 ps). A análise da evolução temporal da poluição por TBT ao longo da costa foi concretizada por meio da comparação entre níveis de organoestanhos em N. reticulatus em amostras de 2008 e 2003 e também através da comparação dos níveis de imposex registados em campanhas realizadas naqueles dois anos. Os resultados obtidos indicam a ocorrência de reduções significativas nas concentrações de TBT, DBT e MBT, assim como uma diminuição significativa nos valores de VDSI entre 2003 e 2008. Os resultados obtidos sugerem que a redução verificada se deve à implementação do Regulamento 782/2003 da Comunidade Europeia, que tem por objectivo a erradicação das descargas e emissões de TBT para o ambiente a partir dos sistemas antivegetativos A diminuição da poluição por TBT ao longo dos últimos anos foi acompanhada por um aumento no número de fêmeas com um vaso deferente, mas sem pénis (imposex do tipo b): 3,5% em 2000, 11% em 2003 e 24% em 2008. Um aumento no número de locais onde se registou o fenómeno também é evidente: dois em 2000, sete em 2003 e treze em 2008. A proporção de fêmeas b no estádio 1 de VDS apresentou igual tendência com aumento de 38% em 2000 para 65% em 2008. O aumento no número de fêmeas com esta via parece estar associado à diminuição da poluição por TBT. Face à esperada diminuição da presença do composto no meio ambiente, devido à sua proibição, o aumento de fêmeas com imposex do tipo b é previsível. A ocorrência de compostos xenoestrogénicos no ambiente aquático foi também estudada e os níveis de estrona (E1), 17α-e 17β-estradiol (E2), 17α- etinilestradiol (EE2), bisfenol-A (BPA) e nonilfenol (NP) foram quantificados em efluentes de estações de tratamento de águas residuais (ETARs) localizadas na região de Aveiro, bem como no efluente final descarregado no Oceano Atlântico, através de um emissário submarino (S. Jacinto), sendo amostras recolhidas na entrada da Ria e ao largo usadas como referência. Os níveis de hormonas esteróides e compostos fenólicos registados nos locais de referência são baixos. De entre as hormonas esteróides os níveis mais elevados foram registados para a estrona, com valores máximos de 85.3 ng.L- 1 . Os níveis mais elevados de compostos fenólicos foram detectados em efluentes industriais (máximos de NP e BPA de 2410 ng.L-1 e 897 ng.L-1 , respectivamente). Os resultados obtidos sugerem que os níveis de compostos xenoestrogénicos em locais de referência são baixos e não parecerem acarretar risco ecológico, no entanto o mesmo não será verdadeiro para as imediações do emissário de S. Jacinto que liberta efluentes com concentrações muito elevadas de E1, NP e BPA. Foram realizadas experiências laboratoriais de forma a elucidar o papel do receptor retinóico X (RXR) no mecanismo de indução de imposex (presentemente o mecanismo que demonstra maior promessa na explicação do desencadear deste fenómeno). Fêmeas de Nucella lapillus e N. reticulatus foram injectadas com TBT em etanol ou com ácido 9-cis- retinóico em FBS (soro fetal bovino) tendo-se procedido à sua observação nos 30 dias subsequentes. Tanto o TBT como o 9CRA induziram o desenvolvimento de imposex em N. lapillus e N. reticulatus. Aumentos significativos nos valores de VDSI e FPL entre o controlo de etanol e o tratamento de TBT e o controlo de FBS e o tratamento de 9CRA foram registados. Os resultados obtidos fornecem novas provas do envolvimento da via de sinalização associada ao RXR no desenvolvimento de imposex em ambas as espécies.
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A new electrochemical methodology to study labile trace metal/natural organic matter complexation at low concentration levels in natural waters is presented. This methodology consists of three steps: (i) an estimation of the complex diffusion coefficient (DML), (ii) determination at low pH of the total metal concentration initially present in the sample, (iii) a metal titration at the desired pH. The free and bound metal concentrations are determined for each point of the titration and modeled with the non-ideal competitive adsorption (NICA-Donnan) model in order to obtain the binding parameters. In this methodology, it is recommended to determine the hydrodynamic transport parameter, α, for each set of hydrodynamic conditions used in the voltammetric measurements. The methodology was tested using two fractions of natural organic matter (NOM) isolated from the Loire river, namely the hydrophobic organic matter (HPO) and the transphilic organic matter (TPI), and a well characterized fulvic acid (Laurentian fulvic acid, LFA). The complex diffusion coefficients obtained at pH 5 were 0.4 ± 0.2 for Pb and Cu/HPO, 1.8 ± 0.2 for Pb/TPI and (0.612 ± 0.009) × 10−10 m2 s−1 for Pb/LFA. NICA-Donnan parameters for lead binding were obtained for the HPO and TPI fractions. The new lead/LFA results were successfully predicted using parameters derived in our previous work.
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Dissertação de mestrado, Biologia Marinha, Faculdade de Ciências e Tecnologia, Universidade do Algarve, 2015
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Tese de doutoramento, Sistemas Sustentáveis de Energia, Universidade de Lisboa, Faculdade de Ciências, 2015
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Purpose To analyse pacing strategies displayed by athletes achieving differing levels of performance during an elite level marathon race. Methods Competitors in the 2009 IAAF Women’s Marathon Championship were split into Groups 1, 2, 3, and 4 comprising the first, second, third, and fourth 25% of finishers respectively. Final, intermediate, and personal best (PB) times of finishers were converted to mean speeds, and relative speed (% of PB speed) was calculated for intermediate segments. Results Mean PB speed decreased from Group 1 to 4 and speed maintained in the race was 98.5 + 1.8%, 97.4 + 3.2%, 95.0 + 3.1% and 92.4 + 4.4% of PB speed for Groups 1-4 respectively. Group 1 was fastest in all segments and differences in speed between groups increased throughout the race. Group 1 ran at lower relative speeds than other groups for the first two 5 km segments, but higher relative speeds after 35km. Significant differences (P<0.01) in the percentage of PB speed maintained were observed between Groups 1 and 4, and 2 and 4 in all segments after 20 km, and Groups 3 and 4 from 20-25 km and 30-35 km. Conclusions Group 1 athletes achieved superior finishing times relative to their PB than athletes in other Groups who selected unsustainable initial speeds resulting in subsequent significant losses of speed. It is suggested that psychological factors specific to a major competitive event influenced decision making by athletes and poor decisions resulted in final performances inferior to those expected based on PB times.
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We used1H-magnetic resonance spectroscopy to noninvasively determine total creatine (TCr), choline-containing compounds (Cho), and intracellular (IT) and extracellular (between-muscle fibers) triglycerides (ET) in three human skeletal muscles. Subjects' (n = 15 men) TCr concentrations in soleus [Sol; 100.2 ± 8.3 (SE) mmol/kg dry wt] were lower (P < 0.05) than those in gastrocnemius (Gast; 125.3 ± 9.2 mmol/kg dry wt) and tibialis anterior (TA; 123.7 ± 8.8 mmol/kg dry wt). The Cho levels in Sol (35.8 ± 3.6 mmol/kg dry wt) and Gast (28.5 ± 3.5 mmol/kg dry wt) were higher (P < 0.001 andP < 0.01, respectively) compared with TA (13.6 ± 2.4 mmol/kg dry wt). The IT values were found to be 44.8 ± 4.6 and 36.5 ± 4.2 mmol/kg dry wt in Sol and Gast, respectively. The IT values of TA (24.5 ± 4.5 mmol/kg dry wt) were lower than those of Sol (P < 0.01) and Gast (P < 0.05). There were no differences in ET [116.0 ± 11.2 (Sol), 119.1 ± 18.5 (Gast), and 91.4 ± 19.2 mmol/kg dry wt (TA)]. It is proposed that the differences in metabolite levels may be due to the differences in fiber-type composition and deposition of metabolites due to the adaptation of different muscles during locomotion.
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Science gateways can provide access to distributed computing resources and applications at very different levels of granularity. Some gateways do not even hide the details of the underlying infrastructure, while on the other end some provide completely customized high-level interfaces to end-users. In this chapter the different granularity levels at which science gateways can be developed with WS-PGRADE/gUSE are analysed. The differences between these various granu-larity levels are also illustrated via the example of a molecular docking gateway and its four different implementations.
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Pesticide exposure during brain development could represent an important risk factor for the onset of neurodegenerative diseases. Previous studies investigated the effect of permethrin (PERM) administered at 34 mg/kg, a dose close to the no observable adverse effect level (NOAEL) from post natal day (PND) 6 to PND 21 in rats. Despite the PERM dose did not elicited overt signs of toxicity (i.e. normal body weight gain curve), it was able to induce striatal neurodegeneration (dopamine and Nurr1 reduction, and lipid peroxidation increase). The present study was designed to characterize the cognitive deficits in the current animal model. When during late adulthood PERM treated rats were tested for spatial working memory performances in a T-maze-rewarded alternation task they took longer to choose for the correct arm in comparison to age matched controls. No differences between groups were found in anxiety-like state, locomotor activity, feeding behavior and spatial orientation task. Our findings showing a selective effect of PERM treatment on the T-maze task point to an involvement of frontal cortico-striatal circuitry rather than to a role for the hippocampus. The predominant disturbances concern the dopamine (DA) depletion in the striatum and, the serotonin (5-HT) and noradrenaline (NE) unbalance together with a hypometabolic state in the medial prefrontal cortex area. In the hippocampus, an increase of NE and a decrease of DA were observed in PERM treated rats as compared to controls. The concentration of the most representative marker for pyrethroid exposure (3-phenoxybenzoic acid) measured in the urine of rodents 12 h after the last treatment was 41.50 µ/L and it was completely eliminated after 96 h.
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Considering tobacco smoke as one of the most health-relevant indoor sources, the aim of this work was to further understand its negative impacts on human health. The specific objectives of this work were to evaluate the levels of particulate-bound PAHs in smoking and non-smoking homes and to assess the risks associated with inhalation exposure to these compounds. The developed work concerned the application of the toxicity equivalency factors approach (including the estimation of the lifetime lung cancer risks, WHO) and the methodology established by USEPA (considering three different age categories) to 18 PAHs detected in inhalable (PM10) and fine (PM2.5) particles at two homes. The total concentrations of 18 PAHs (ΣPAHs) was 17.1 and 16.6 ng m−3 in PM10 and PM2.5 at smoking home and 7.60 and 7.16 ng m−3 in PM10 and PM2.5 at non-smoking one. Compounds with five and six rings composed the majority of the particulate PAHs content (i.e., 73 and 78 % of ΣPAHs at the smoking and non-smoking home, respectively). Target carcinogenic risks exceeded USEPA health-based guideline at smoking home for 2 different age categories. Estimated values of lifetime lung cancer risks largely exceeded (68–200 times) the health-based guideline levels at both homes thus demonstrating that long-term exposure to PAHs at the respective levels would eventually cause risk of developing cancer. The high determined values of cancer risks in the absence of smoking were probably caused by contribution of PAHs from outdoor sources.