Investigation on microstructure and oxidation behavior of Cr-modified aluminide coating on γ-TiAl alloys

Microstructure and oxidation behavior of aluminide coating has been investigated. The layers were examined by optical microscopy, scanning electron microscopy (SEM) equipped with EDS and X-ray diffraction method. The isothermal oxidation behaviors of samples were investigated at 950°C for 200 h. The results indicated that TiAl₃ were formed on substrate. In addition, aluminide coating improved the oxidation resistance of γ-TiAl alloys by forming a protective alumina scale. Moreover, during oxidation treatment the interdiffusion of TiAl₃ layer with γ-TiAl substrate results in depletion of aluminum in the TiAl₃ layer and growth of TiAl₂ layer. After oxidation treatment the coating layer maintained a microstructure with phases including TiAl₃, TiAl₂ and Al₂O₃.Досліджено мікроструктуру алюмінідного покриву та його поведінку під час високотемпературного окислення. Шари алюмінідів титану вивчали за допомогою оптичної мікроскопії, сканівної електронної мікроскопії (SЕМ) з використанням дисперсного рентгеноспектрометра (EDS) та рентгенівським дифракційним методом. Випробовування проводили при 950°C впродовж 200 h. Встановлено, що на підкладці з титанового сплаву утворився TiAl₃. Покрив з алюмініду титану покращує стійкість до окислення сплавів з γ-TiAl, утворюючи захисну плівку з оксиду алюмінію. Під час окислення дифузійна взаємодія TiAl₃ з підкладкою γ-TiAl спричиняє зменшення кількості алюмінію у шарі TiAl₃ та збільшення шару TiAl₂. Після окислення в покриві утворюється мікроструктура з фазами, що містять TiAl₃, TiAl₂ та Al₂O₃.Исследовано микроструктуру алюминидного покрытия и его поведение при высокотемпературном окислении. Слои алюминида титана изучали с помощью оптической микроскопии, сканирующей электронной микроскопии (SЕМ) с использованием дисперсного рентгеноспектрометра (EDS) и рентгеновским дифракционным методом. Испытания проводили при 950°C в течение 200 h. Установлено, что на подкладке из титанового сплава образовался TiAl₃. Покрытие из алюминида титана улучшает стойкость к окислению сплавов из γ-TiAl, образовывая защитную пленку из окисла алюминия. Во время окисления диффузионное взаимодействие TiAl₃ с подкладкой γ-TiAl влечет уменьшение количества алюминия в слое TiAl₃ и увеличение слоя TiAl₂. После окисления в покрытии образуется микроструктура с фазами, которые содержат TiAl₃, TiAl₂ и Al₂O₃

Étude des blooms toxiques à cyanobactéries dans trois lacs réservoirs du Maroc : résultats préliminaires

Dans le cadre du programme de recherche sur les blooms toxiques à cyanobactéries dans certains lacs de barrage du Maroc, une étude de ce phénomène a été entreprise sur trois retenues : Lalla Takerkoust, Oued Mellah et Al Massira. L'étude taxonomique montre que dans les lacs Lalla Takerkoust et Al Massirra, l'espèce responsable des blooms est Microcystis aeruginosa alors que dans la retenue saumâtre et hypereutrophe Oued Mellah, c'est Microcystis ichthyoblabe.En complément, une étude toxicologique et toxinologique a permis d'évaluer les risques sanitaires potentiels qui peuvent être engendrés par ces blooms. L'hépatotoxicité, pour l'ensemble des blooms récoltés en 1999, a été confirmée par le biotest " souris ". L'application de ce test a montré que le bloom de LallaTakerkoust est hautement toxique (DL50 500 mg/kg) et celui d'Al Massira est intermédiaire (DL50 comprise entre 100 et 500 mg/kg). Les teneurs en microcystines (hépatotoxines) déterminées par ELISA révèlent des concentrations beaucoup plus importantes pour le bloom de Lalla Takerkoust. L'utilisation de la chromatographie liquide haute performance avec détecteur à barrette photodiode, (CLHP-DBP) a permis la détection et l'identification de 2, 4 et 11 variantes de microcystines, respectivement à partir d'extraits du bloom naturel d'Al Massira, Lalla Takerkoust et Oued Mellah. Cependant, la Microcystine-LR n'a été détectée que dans les extraits d'Al Massira et de Takerkoust. L'apparition des blooms toxiques à cyanobactéries dans ces plans d'eau impose dorénavant la prise en considération des nuisances écologiques et des risques sanitaires liés à la présence des microcystines dans ces eaux.During the first part of the toxic cyanobacteria survey program carried out since 1994, Microcystis blooms which periodically occurred in Al Massira, Lalla Takerkoust and Oued Mellah reservoirs were studied. These reservoirs were located at a different hydrographic basin and have a various trophic status. The water was used for irrigation, recreational purpose and/or drinking water supply. The bloom-forming species was identified as Microcystis aeruginosa in Al Massira and Takerkoust freshwater reservoirs whereas in brackish water Oued Mellah reservoir, the bloom-forming species is Microcystis ichthyoblabe.In complement to this ecological studies and in order to assess the potential health risk, a toxicology and toxinology of these Microcystis blooms were undertaken. The hepatotoxicity of lyophilized bloom material collected during bloom periods in 1999 was confirmed by (i. p) mice bioassay. The toxicity assessment revealed that Microcystis Takerkoust bloom was highly toxic with LD50 < 100 mg/kg whereas those from Al Massira and Oued Mellah were respectively characterized by a medium and a low toxicities.The content of microcystins (MCYST) determined by the Enzyme-linked Immunosorbent assay (ELISA) show that MCYST content ranged between 0.37 to 496 µg/g dry weight. It appears that Takerkoust bloom contain 600 to 1300 fold more MCYST than Oued Mellah and Al Massira blooms. The isolation and identification of microcystins variants from bloom extracts were performed using the high performance liquid chromatography with photodiode array detection (HPLC-PDA). This technique provided the separation and identification of at least two microcytins variants from each bloom material. The most number of 11 microcystins were detected from Microcystis ichthyoblabe bloom of Oued Mellah. However, only two and four variants of microcystins were respectively detected from Al Massira and Takerkoust blooms. Among these variants of microcystins solely Microcystin-LR was identified according to the Mcyst-LR authentic sample from extract of Al Massira and Takerkoust blooms.The occurrence of toxic cyanobacteria bloom in these drinking and/or recreational water reservoirs lead us to take into consideration the real health hazard which will be induced by these harmful cyanobacterial blooms

Application de certains indices diatomiques à un cours d'eau marocain : Oued Hassar

Les eaux de l'Oued Hassar (Maroc) sont caractérisées par une forte minéralisation. La conductivité, variant entre 3470 et 7210 µS.cm-1, est due essentiellement aux fortes teneurs en chlorures. L'examen de l'Indice de Pollution Organique (IPO) montre que l'effluent d'eaux usées provenant de la ville de Mediouna constitue la principale source de pollution des eaux de l'Oued Hassar.Concernant l'étude des diatomées épilithiques, 61 espèces et variétés de diatomées ont été inventoriées. Ces taxons sont liés particulièrement à la salinité (Pleurosira laevis, Fragilaria pulchella,…) et à la charge organique (Nitzschia palea, Gomphonema parvulum,…).Quatre indices diatomiques ont été testés pour l'évaluation de la qualité des eaux de l'Oued Hassar : l'Indice Diatomique Pratique (IDP), l'Indice Diatomique Générique (IDG), l'Indice de Sládecek (SLA) et l'Indice Diatomique Trophique (IDT). La variation spatio-temporelle de ces indices reflète bien la dégradation de la qualité de ce cours d'eau, particulièrement en aval du rejet de la ville de Mediouna (IDP=3,86 ± 1,84 ; IDG=6,05 ± 1,95 ; SLA=4,35 ± 1,93 ; IDT=5,80 ± 1,31). Parmi ces indices testés, seul l'IDP présente une corrélation significative (0,63 ; α<5%) avec l'IPO (indice de référence) tandis que l'IDG, le SLA et l'IDT montrent des corrélations non significatives avec cet indice (0,38 ; 0,27 et -0,11 respectivement).The water quality in Moroccan rivers and streams becomes more and more injured because of the important amount of pollutants discharged in these aquatic ecosystems without any treatment in the most cases. A physical, chemical and microbiological analyses are regularly done by public institutions (office national des eaux potables, direction de l'hydrolique). However, these analyses become insufficient facing the big diversity of chemicals and the intermittence of pollution sources at the time. So, methods using a biotic indicators as a complement of the chemical analyses become a requirement in the water quality assessment. In the present study, besides the physical and chemical analyses, we have tested the use of benthic diatoms as indicators of the oued Hassar water quality and diatom indices as a tool for the evaluation of this quality.Oued Hassar is a canalized stream situated on the valley of oued Mellah river. It drains a part of the Berrechid groundwater as sources. Its main source (station SC) is situated to 3 km in the Northeast of Mediouna (155 m). Along this water course, in sections of various degrees of water pollution, six sites (SC, SB, HP, OM, SH and CA) were sampled on four different dates (august 1997 and january, june and august 1998). The station OM belongs to oued Mouileh stream which is a unique tributary of oued Hassar. The main source of pollution; the wastewater effluent of Médiouna agglomeration entered the stream between The oued Hassar source and the station SB (Sidi Brahim). This region has a Mediterranean semi-aride bioclimate. The influence of the ocean results in a summer temperatures generally varying between 25 and 30°C and winter temperatures varying between 12 and 19°C.The physical and chemical analysis data of the oued Hassar waters show particularly elevated values of water conductivity essentially due to the high contents in chlorides. These values were understood between a minimal value recorded at station SH in August 1998 (3470 mS.cm-1) and a maximal value signalled at station OM in January of the same year (7210 mS.cm-1). Concentrations in sulphates vary according to stations. The most elevated values were recorded in january 1998 at stations SC and OM (231 and 218 mg.l-1 respectively). The hardness values are very important especially at the source of oued Hassar (SC) where the concentration reaches 25,2 meq.l-1. This excessive mineralization of waters, particularly at stations SC and OM, is essentially due to the Permo-triasique saliferous sedimentary layers which crop out in the area.The oued Hassar stream receives, to 100 ms downstream the station SC, the wastewater effluent of Médiouna agglomeration, highly loaded with organic matters, ammonia, orthophosphates and suspended matters. The impact of this effluent results on the elevated values of these parameters downstream the wastewater input (SB). On January 1998 (rainy period), the important contents in orthophosphates and sulphates recorded at all stations were essentially due to the high amounts of superphosphates and ammonia sulphates used as amendment of the cultivated lands situated a long the sides of oued Hassar stream.Outside of this period, contents in orthophosphates and ammonia at stations SC and OM are very low. However, the elevated content in nitrates at the oued Hassar's source (maximal value: 93,3 mg.l-1) gives an idea on the deterioration of the groundwater quality.To put in evidence the evolution of the global organic pollution of waters, the "Indice de Pollution Organique" (IPO) have been calculated. The exam of this index shows that the wastewater effluent constitutes the main source of pollution. Indeed, water quality goes from a mean pollution state (3,88 ± 0,14) at the oued Hassar's source to a very strong pollution state (1,96 ± 0,31) at the station SB. Downstream the swampy zone, at the station HP, the water quality of oued Hassar improves remarkably (3,50 ± 0,74) due to the auto-purification phenomenon and the dilution of these waters by those coming from the secondary sources situated between stations SB and HP. At the stations SH and CA, the IPO mean values (3,50 ± 0,79 and 3,75 ± 0,41 respectively) show that the water quality remains rather identical as at the station HP.Concerning the survey of epilithic diatoms, 61 species and varieties of diatoms have been inventoried. These taxa are bound especially to the salinity (Amphora coffeaeformis, Fragilaria fasciculata, Fragilaria pulchella, Pleurosira laevis,…) and to the organic load (Gomphonema parvulum, Navicula subminuscula, Nitzschia palea,…). In the most collected samples, particularly at the stations SB, SH and CA, diatom communities are essentially dominated by N. palea and the complex N. inconspicua / N. frustulum. At the station SB, the relative abundance of N. palea reaches 71% in august 1997 and august 1998, and goes beyond 45% in January and june 1998. giving evidence of the important organic pollution. this species is substituted, at stations SH and CA, essentially by Navicula subminuscula, N. veneta and Nitzschia inconspicua / N. frustulum complex. Diatom communities at the stations SC, HP and OM don't show an exclusive dominance of one or two species, but several species dominate and form a more varied communities.Four diatom indices have been tested to assess the water quality in Oued Hassar (Morocco) : the "Indice Diatomique Pratique" (IDP), the "Indice Diatomique Générique" (IDG), the Sládecek Index (SLA) and the Trophic Diatom Index (TDI). These indices are different by the assigned indicative values and pollution sensitivity coefficients relative to every species and by the taxonomic list integrated in the calculation of every index. The spatio-temporal variation of these indices reflects clearly the deterioration of water quality downstream the wastewater input of Mediouna agglomeration (IDP=3,86 ± 2,30; IDG=6,05 ± 2,31; SLA=4,35 ± 2,62; IDT=5,80 ± 1,85) and its recovery after the swampy zone at the station HP (IDP=9,37 ± 2,35; IDG=11,83 ± 1,77 ; SLA=7,19 ± 3,05 ; IDT=6,76 ± 2,48). Among these indices, only the IDP presents a significant correlation (0,63 ; α<5%) with the IPO (reference index). While the IDG, the SLA and the TDI don't show a significant correlation with this index (0,38 ; 0,27 and -0,11 respectively). The IDT shows nearly the same water quality in the different stations and rather inform on the high level of eutrophication in these water courses.The physical and chemical analyses, the composition of diatom communities as well as the relative results of diatom indices, show that the oued Hassar stream is submitted to an important pollution, particularly downstream the wastewater input. Among the tested indices, the IDP appears more adapted to the assessment of water quality in oued Hassar. However, more work is required in order to finalize a new diatom index which is more adapted to characteristics of the Moroccan water courses

catena-Poly[[(2,9-dimethyl-1,10-phenanthroline-κ2 N,N′)lead(II)]-di-μ-bromido]

In the title compound, [PbBr2(C14H12N2)]n, the PbII atom lies on a twofold rotation axis. The N-heterocycle-chelated PbII atom exists in a distorted octa­hedral geometry owing to two long Pb⋯Br inter­actions [2.9562 (5) and 3.2594 (5) Å]. These result in a zigzag chain running along the c axis. The lone pair is stereochemically inactive

SYNTHESIS, ANTITUMOR ACTIVITY, PHARMACOPHORE MODELING AND QSAR STUDIES OF NOVEL PYRAZOLES AND PYRAZOLO [1, 5-A] PYRIMIDINES AGAINST BREAST ADENOCARCINOMA MCF-7 CELL LINE

Objective: The present work aimed to synthesize New series of pyrazoles 3 and pyrazolo[1,5-a]pyrimidines 5, 7, 9 in order to evaluate their antiproliferative activity against human breast adenocarcinoma MCF-7cell line and study the cell cycle progression of the most active compounds. In addition, Pharmacophore modeling and QSAR Studies of these new compounds were done.Methods: The diazonium salt of 4-aminoacetophenone 1 was coupled with malononitrile in ethanol using sodium acetate affords 2-[(4-acetylphenyl)diazenyl] malononitrile Cycloaddition of hydrazine hydrate, in molar ratios 1:1 or 1:2, on compound 2, furnished 3,5-diaminopyrazolederivatives 3a and 3b respectively. Moreover, new pyrazolo[1,5-a]pyrimidine derivatives 5a-f were obtained upon cyclocondensation of 3a, b with different chalcones 4a-c in EtOH/piperidine,while compounds 7a-f were prepared via cycloaddition of 3a, b with various arylidene malononitriles 6a-c in the same reaction condition. Finally, treatment of 3a, b with ethyl 2-cyano-3-ethoxyacrylate 8a or 2-(ethoxymethylene)malononitrile 8b in EtOH/TEA yielded the novel pyrazolo[1,5-a]pyrimidine derivatives 9a, b respectively. These target compounds were screened for their cytotoxic activity against MCF-7 (human breast Cell Line) followed by study cell cycle of 7a. Finally, Pharmacophore modeling and QSAR Studies was carried out.Results: The pyrazolopyrimidine 7a was the most active compound (IC50 = 3.25 µM), whereas, some of the tested compounds exploited moderate growth inhibitory activity. Its effect was further studied on cell cycle progression; results showed that compound 7a induced cell cycle arrest at S-phase verifying this compound as a promising selective anticancer agent.Conclusion: Compound 7a was found to be the most active member against MCF-7 breast cancer (IC50= 3.25 μM), Further biological assessment of 7a using flow-cytometric analysis, revealed that it induced cell cycle arrest at S phase.Keywords: Pyrazole, Pyrazolo[1,5-a]pyrimidine, MCF-7 breast cancer cell line, Cell cycle profile, 3D pharmacophore,1 QSAR stud

Stochastic Processes in Yellow and Red Pulsating Variables

Random changes in pulsation period are well established in cool pulsating stars, in particular the red giant variables: Miras, semi-regulars of types A and B, and RV Tau variables. Such effects are also observed in a handful of Cepheids, the SX Phe variable XX Cyg, and, most recently, the red supergiant variable, BC Cyg, a type C semi-regular. The nature of such fluctuations is seemingly random over a few pulsation cycles of the stars, yet the regularity of the primary pulsation mechanism dominates over the long term. The degree of stochasticity is linked to the dimensions of the stars, the randomness parameter 'e' appearing to correlate closely with mean stellar radius through the period 'P', with an average value of e/P = 0.0136+-0.0005. The physical processes responsible for such fluctuations are uncertain, but presumably originate in temporal modifications of envelope convection in such stars.Comment: Poster given at the "Stellar Pulsation: Challenges for Theory and Observation" conference in Santa Fe, New Mexico (2009

Premier rapport sur la prolifération de marées jaunes ichthyotoxiques à Prymnesium parvum Carter (Haptophyceae) dans le lac hypereutrophe Oued Mellah (Maroc)

Les algues Prymnesiophyceae ou Haptophyceae (Chrysophyta) renferment des espèces capables de pullulations spectaculaires nommées " marées jaunes ". Parmi les Haptophycées, les plus communes sont : Prymnesium parvum, Prymnesium patelliferum et Chrysochromulina polylepis. Ces microalgues ont été souvent incriminées dans des cas de mortalité aiguë de poissons et d'invertébrés aquatiques. P. parvum est connue depuis cent ans comme responsable de blooms toxiques ayant entraîné des mortalités catastrophiques de poissons dans diverses régions du monde.Au Maroc, ces blooms à Prymnesiophyceae n'ont, jusqu'à présent, jamais été signalés. Nos recherches sur les successions phytoplanctoniques du lac hypereutrophe et saumâtre de Oued Mellah (33°30'N-07°20'W), ont mis en évidence la prolifération périodique en automne de l'Haptophycée P. parvum occasionnant des blooms spectaculaires. Les densités cellulaires de P. parvum, espèce dominante, atteignent des maxima de 148·106 cellules·L-1 en 1998 et 169·106 cellules·L-1 en 1999, représentant 34 à 80 % de la biomasse totale. Ces " marées jaunes " coïncident régulièrement avec des mortalités catastrophiques de poissons et d'invertébrés aquatiques dans le lac laissant présager une toxicité aiguë de cette souche de microalgue.Dans ce travail sont présentés les premiers résultats concernant la dynamique interannuelle des blooms à P. parvum et l'influence des conditions physicochimiques particulières des eaux du lac sur leur développement est discutée.The Prymnesiophyceae or Haptophyceae (Chrysophyta) contain species-forming spectacular blooms named yellow tides. Among Haptophyceae, Prymnesium parvum, Prymnesium patelliferum and Chrysochromulina polylepis are the most common. These microalgae were often involved in acute fish and aquatic invertebrates mortality cases. P. parvum, known since hundred years as being responsible for toxic blooms, has induced catastrophic fish mortality in various areas throughout the world.In Morocco, blooms of Prymnesiophyceae have never been reported up till now. Studies on phytoplankton successions in the hypertrophic brackish Oued Mellah lake (33°30'N-07°20'W) show a periodic autumnal proliferation of P. parvum. This species, which cellular densities reach a maxima of 148·106 cells·L-1 in 1998 and 169·106 cells·L-1 in 1999, dominates the other phytoplanctonic species with 34 to 80% of the total biomass. The yellow tides coincide regularly with dramatic fish and aquatic invertebrates mortality in the lake leading to the prediction of an acute toxicity due to this microalgae.The principal aim of this study was to present the first results concerning the interannual dynamics of P. parvum blooms and to discuss the influence of the particular physical and chemical water characteristics on their development