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Evapotranspiration (ET) plays an important role in global climate dynamics and in primary production of terrestrial ecosystems; it represents the mass and energy transfer from the land to atmosphere. Limitations to measuring ET at large scales using ground-based methods have motivated the development of satellite remote sensing techniques. The purpose of this work is to evaluate the accuracy of the SEBAL algorithm for estimating surface turbulent heat fluxes at regional scale, using 28 images from MODIS. SEBAL estimates are compared with eddy-covariance (EC) measurements and results from the hydrological model MGB-IPH. SEBAL instantaneous estimates of latent heat flux (LE) yielded r(2) = 0.64 and r(2) = 0.62 over sugarcane croplands and savannas when compared against in situ EC estimates. At the same sites, daily aggregated estimates of LE were r(2) = 0.76 and r(2) = 0.66, respectively. Energy balance closure showed that turbulent fluxes over sugarcane croplands were underestimated by 7% and 9% over savannas. Average daily ET from SEBAL is in close agreement with estimates from the hydrological model for an overlay of 38,100 km(2) (r(2) = 0.88). Inputs to which the algorithm is most sensitive are vegetation index (NDVI), gradient of temperature (dT) to compute sensible heat flux (H) and net radiation (Re). It was verified that SEBAL has a tendency to overestimate results both at local and regional scales probably because of low sensitivity to soil moisture and water stress. Nevertheless the results confirm the potential of the SEBAL algorithm, when used with MODIS images for estimating instantaneous LE and daily ET from large areas.

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FUNDAMENTO: Sabe-se que hábitos de vida inadequados favorecem a hipertensão, e os adventistas preconizam hábitos saudáveis. OBJETIVO: Avaliar a prevalência da hipertensão nos adventistas do sétimo dia na capital e no interior paulistas. MÉTODOS: Foram estudados 264 adventistas (41,17 ± 15,27 anos, 59,8% mulheres, com alto nível de religiosidade avaliada pela escala Duke-DUREL). A medida da pressão arterial foi realizada com aparelho automático validado. Nível de significância adotado foi p < 0,05. Resultados: A prevalência total de hipertensão foi 22,7%, (27,4% no interior e 15% na capital). Os adventistas da capital diferiram dos do interior (p < 0,05), respectivamente, quanto: escolaridade superior (62% vs 36,6%); ter vínculo empregatício (44%) vs autônomos (40,9%); renda familiar (8,39 ± 6,20 vs 4,59 ± 4,75 salários mínimos) e renda individual (4,54 ± 5,34 vs 6,35 ± 48 salários mínimos); casal responsável pela renda familiar (35% vs 39,6%); vegetarianismo (11% vs 3%); pressão arterial (115,38 ± 16,52/68,74 ± 8,94 vs 123,66 ± 19,62/74,88 ± 11,85 mmHg); etnia branca (65% vs 81,1%); casados (53% vs 68,9%); menor apoio social no domínio material (15,7 ± 5,41 vs 16,9 ± 4,32) e lembrar da última vez que mediu a pressão arterial (65% vs 48,8%). A análise multivariada associou hipertensão com: 1) vegetarianismo (OR 0,051, IC95% 0,004-0,681), 2) escolaridade (OR 5,317, IC95% 1,674-16,893), 3) lembrar quando mediu a pressão (OR 2,725, IC95% 1,275-5,821), 4) aposentado (OR 8,846, IC95% 1,406-55,668), 5) responsável pela renda familiar (OR 0,422, IC95% 0,189-0,942). CONCLUSÃO: A prevalência de hipertensão dos adventistas foi menor se comparada com estudos nacionais, sendo menor na capital em relação ao interior possivelmente por melhores condições socioeconômicas e hábitos de vida.

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[EN]This is the first time that the reproductive characteristics of Mycteroperca fusca have been analyzed over the whole area of its distribution, using the parameter of the histological analysis of the gonads. This species is a protogynous hermaphrodite with a marked predominance of females (1:4.9). The males and females displayed marked differences in the distribution of the sizes. The females were distributed over all the size ranges analyzed (229-725 mm total length), whereas the males were observed within the larger sizes, as of 428 mm. One transitional specimen (610 mm total length) was observed. The size at which the females first reached sexual maturity was 335 mm total length whereas the size at which 95% of females reached sexual maturity was 398 mm total length. The average size at which 50% of the females had inverted to the male condition was found to be 678 mm total length. The range of sizes at which the process of sexual inversion took place was broad, between 428 and 725 mm total length. The reproductive period was long, almost covering the annual cycle, although the maximum activity was observed between April and October, with a peak in spawning in June-July.

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Organizan el ciclo de conferencias el Centro de Formación de la Cooperación Española en Cartagena de Indias con la colaboración de Cátedra UNESCO de Planificación Turística y Desarrollo Sostenible de la Universidad de Las Palmas de Gran Canaria -Tides-

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Introduction 1.1 Occurrence of polycyclic aromatic hydrocarbons (PAH) in the environment Worldwide industrial and agricultural developments have released a large number of natural and synthetic hazardous compounds into the environment due to careless waste disposal, illegal waste dumping and accidental spills. As a result, there are numerous sites in the world that require cleanup of soils and groundwater. Polycyclic aromatic hydrocarbons (PAHs) are one of the major groups of these contaminants (Da Silva et al., 2003). PAHs constitute a diverse class of organic compounds consisting of two or more aromatic rings with various structural configurations (Prabhu and Phale, 2003). Being a derivative of benzene, PAHs are thermodynamically stable. In addition, these chemicals tend to adhere to particle surfaces, such as soils, because of their low water solubility and strong hydrophobicity, and this results in greater persistence under natural conditions. This persistence coupled with their potential carcinogenicity makes PAHs problematic environmental contaminants (Cerniglia, 1992; Sutherland, 1992). PAHs are widely found in high concentrations at many industrial sites, particularly those associated with petroleum, gas production and wood preserving industries (Wilson and Jones, 1993). 1.2 Remediation technologies Conventional techniques used for the remediation of soil polluted with organic contaminants include excavation of the contaminated soil and disposal to a landfill or capping - containment - of the contaminated areas of a site. These methods have some drawbacks. The first method simply moves the contamination elsewhere and may create significant risks in the excavation, handling and transport of hazardous material. Additionally, it is very difficult and increasingly expensive to find new landfill sites for the final disposal of the material. The cap and containment method is only an interim solution since the contamination remains on site, requiring monitoring and maintenance of the isolation barriers long into the future, with all the associated costs and potential liability. A better approach than these traditional methods is to completely destroy the pollutants, if possible, or transform them into harmless substances. Some technologies that have been used are high-temperature incineration and various types of chemical decomposition (for example, base-catalyzed dechlorination, UV oxidation). However, these methods have significant disadvantages, principally their technological complexity, high cost , and the lack of public acceptance. Bioremediation, on the contrast, is a promising option for the complete removal and destruction of contaminants. 1.3 Bioremediation of PAH contaminated soil & groundwater Bioremediation is the use of living organisms, primarily microorganisms, to degrade or detoxify hazardous wastes into harmless substances such as carbon dioxide, water and cell biomass Most PAHs are biodegradable unter natural conditions (Da Silva et al., 2003; Meysami and Baheri, 2003) and bioremediation for cleanup of PAH wastes has been extensively studied at both laboratory and commercial levels- It has been implemented at a number of contaminated sites, including the cleanup of the Exxon Valdez oil spill in Prince William Sound, Alaska in 1989, the Mega Borg spill off the Texas coast in 1990 and the Burgan Oil Field, Kuwait in 1994 (Purwaningsih, 2002). Different strategies for PAH bioremediation, such as in situ , ex situ or on site bioremediation were developed in recent years. In situ bioremediation is a technique that is applied to soil and groundwater at the site without removing the contaminated soil or groundwater, based on the provision of optimum conditions for microbiological contaminant breakdown.. Ex situ bioremediation of PAHs, on the other hand, is a technique applied to soil and groundwater which has been removed from the site via excavation (soil) or pumping (water). Hazardous contaminants are converted in controlled bioreactors into harmless compounds in an efficient manner. 1.4 Bioavailability of PAH in the subsurface Frequently, PAH contamination in the environment is occurs as contaminants that are sorbed onto soilparticles rather than in phase (NAPL, non aqueous phase liquids). It is known that the biodegradation rate of most PAHs sorbed onto soil is far lower than rates measured in solution cultures of microorganisms with pure solid pollutants (Alexander and Scow, 1989; Hamaker, 1972). It is generally believed that only that fraction of PAHs dissolved in the solution can be metabolized by microorganisms in soil. The amount of contaminant that can be readily taken up and degraded by microorganisms is defined as bioavailability (Bosma et al., 1997; Maier, 2000). Two phenomena have been suggested to cause the low bioavailability of PAHs in soil (Danielsson, 2000). The first one is strong adsorption of the contaminants to the soil constituents which then leads to very slow release rates of contaminants to the aqueous phase. Sorption is often well correlated with soil organic matter content (Means, 1980) and significantly reduces biodegradation (Manilal and Alexander, 1991). The second phenomenon is slow mass transfer of pollutants, such as pore diffusion in the soil aggregates or diffusion in the organic matter in the soil. The complex set of these physical, chemical and biological processes is schematically illustrated in Figure 1. As shown in Figure 1, biodegradation processes are taking place in the soil solution while diffusion processes occur in the narrow pores in and between soil aggregates (Danielsson, 2000). Seemingly contradictory studies can be found in the literature that indicate the rate and final extent of metabolism may be either lower or higher for sorbed PAHs by soil than those for pure PAHs (Van Loosdrecht et al., 1990). These contrasting results demonstrate that the bioavailability of organic contaminants sorbed onto soil is far from being well understood. Besides bioavailability, there are several other factors influencing the rate and extent of biodegradation of PAHs in soil including microbial population characteristics, physical and chemical properties of PAHs and environmental factors (temperature, moisture, pH, degree of contamination). Figure 1: Schematic diagram showing possible rate-limiting processes during bioremediation of hydrophobic organic contaminants in a contaminated soil-water system (not to scale) (Danielsson, 2000). 1.5 Increasing the bioavailability of PAH in soil Attempts to improve the biodegradation of PAHs in soil by increasing their bioavailability include the use of surfactants , solvents or solubility enhancers.. However, introduction of synthetic surfactant may result in the addition of one more pollutant. (Wang and Brusseau, 1993).A study conducted by Mulder et al. showed that the introduction of hydropropyl-ß-cyclodextrin (HPCD), a well-known PAH solubility enhancer, significantly increased the solubilization of PAHs although it did not improve the biodegradation rate of PAHs (Mulder et al., 1998), indicating that further research is required in order to develop a feasible and efficient remediation method. Enhancing the extent of PAHs mass transfer from the soil phase to the liquid might prove an efficient and environmentally low-risk alternative way of addressing the problem of slow PAH biodegradation in soil.

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Water resources management will become increasingly important in agriculture as global warming takes place. Cover crop is largely used in viticultural areas based on the many positive agronomic and environmental benefits it provides. However, it is not clear what effect the cover crop can have on water use in the vineyard. This study is designed to develop a further understanding of the role cover crops play in total water use in the vineyard and develop our understanding of the potential use of cover crops as a water management tool. Two techniques were used to measure cover crop water use, the mini-lysimeters and a portable open chamber and data from both was compared to reference evapotranspiration (ETo) (FAO guidelines). While the mini-lysimeters seemed to be limited in their ability to accurately represent the water use of the surrounding soil, the open chamber method is a reliable and suitable instrument to be used for the accurate measurement of evapotranspiration. Further, the relationship between vineyard grass water use and the contributing environmental factors thought to influence water use were analyzed. A strong relationship between total available radiation and cover crop evapotranspiration was found suggesting the possibility of an indirect method of evapotranspiration measurement in a vineyard grass cover crop. Mowing the cover crop was determined to significantly effect transpiration as shown by both the mini-lysimeter and open chamber, however, the reduction was largely dependent on the growth rate of the grass.

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[ES]This paper describes some simple but useful computer vision techniques for human-robot interaction. First, an omnidirectional camera setting is described that can detect people in the surroundings of the robot, giving their angular positions and a rough estimate of the distance. The device can be easily built with inexpensive components. Second, we comment on a color-based face detection technique that can alleviate skin-color false positives. Third, a simple head nod and shake detector is described, suitable for detecting affirmative/negative, approval/dissaproval, understanding/disbelief head gestures.

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ABSTRACTDie vorliegende Arbeit befasste sich mit der Reinigung,heterologen Expression, Charakterisierung, molekularenAnalyse, Mutation und Kristallisation des EnzymsVinorin-Synthase. Das Enzym spielt eine wichtige Rolle inder Ajmalin-Biosynthese, da es in einerAcetyl-CoA-abhängigen Reaktion die Umwandlung desSarpagan-Alkaloids 16-epi-Vellosimin zu Vinorin unterBildung des Ajmalan-Grundgerüstes katalysiert. Nach der Reinigung der Vinorin-Synthase ausHybrid-Zellkulturen von Rauvolfia serpentina/Rhazya strictamit den fünf chromatographischen TrennmethodenAnionenaustauschchromatographie an SOURCE 30Q, HydrophobeInteraktionen Chromatographie an SOURCE 15PHE,Chromatographie an MacroPrep Ceramic Hydroxyapatit,Anionenaustauschchromatographie an Mono Q undGrößenausschlußchromatographie an Superdex 75 konnte dieVinorin-Synthase aus 2 kg Zellkulturgewebe 991fachangereichert werden.Das nach der Reinigung angefertigte SDS-Gel ermöglichte eineklare Zuordnung der Protein-Bande als Vinorin-Synthase.Der Verdau der Enzymbande mit der Endoproteinase LysC unddie darauffolgende Sequenzierung der Spaltpeptide führte zuvier Peptidsequenzen. Der Datenbankvergleich (SwissProt)zeigte keinerlei Homologien zu Sequenzen bekannterPflanzenenzyme. Mit degenerierten Primern, abgeleitet voneinem der erhaltenen Peptidfragmente und einer konserviertenRegion bekannter Acetyltransferasen gelang es, ein erstescDNA-Fragment der Vinorin-Synthase zu amplifizieren. Mit derMethode der RACE-PCR wurde die Nukleoidsequenzvervollständigt, was zu einem cDNA-Vollängenklon mit einerGröße von 1263 bp führte, der für ein Protein mit 421Aminosäuren (46 kDa) codiert.Das Vinorin-Synthase-Gen wurde in den pQE2-Expressionsvektorligiert, der für einen N-terminalen 6-fachen His-tagcodiert. Anschließend wurde sie erstmals erfolgreich in E.coli im mg-Maßstab exprimiert und bis zur Homogenitätgereinigt. Durch die erfolgreiche Überexpression konnte dieVinorin-Synthase eingehend charakterisiert werden. DerKM-Wert für das Substrat Gardneral wurde mit 20 µM, bzw.41.2 µM bestimmt und Vmax betrug 1 pkat, bzw. 1.71 pkat.Nach erfolgreicher Abspaltung des His-tags wurden diekinetischen Parameter erneut bestimmt (KM- Wert 7.5 µM, bzw.27.52 µM, Vmax 0.7 pkat, bzw. 1.21 pkat). Das Co-Substratzeigt einen KM- Wert von 60.5 µM (Vmax 0.6 pkat). DieVinorin-Synthase besitzt ein Temperatur-Optimum von 35 °Cund ein pH-Optimum bei 7.8.Homologievergleiche mit anderen Enzymen zeigten, dass dieVinorin-Synthase zu einer noch kleinen Familie von bisher 10Acetyltransferasen gehört. Alle Enzyme der Familie haben einHxxxD und ein DFGWG-Motiv zu 100 % konserviert. Basierendauf diesen Homologievergleichen und Inhibitorstudien wurden11 in dieser Proteinfamilie konservierte Aminosäuren gegenAlanin ausgetauscht, um so die Aminosäuren einer in derLiteratur postulierten katalytischen Triade(Ser/Cys-His-Asp) zu identifizieren.Die Mutation aller vorhandenen konservierten Serine undCysteine resultierte in keiner Mutante, die zumvollständigen Aktivitätsverlust des Enzyms führte. Nur dieMutationen H160A und D164A resultierten in einemvollständigen Aktivitätsverlust des Enzyms. Dieses Ergebniswiderlegt die Theorie einer katalytischen Triade und zeigte,dass die Aminosäuren H160A und D164A exklusiv an derkatalytischen Reaktion beteiligt sind.Zur Überprüfung dieser Ergebnisse und zur vollständigenAufklärung des Reaktionsmechanismus wurde dieVinorin-Synthase kristallisiert. Die bis jetzt erhaltenenKristalle (Kristallgröße in µm x: 150, y: 200, z: 200)gehören der Raumgruppe P212121 (orthorhombisch primitiv) anund beugen bis 3.3 Å. Da es bis jetzt keine Kristallstruktureines zur Vinorin-Synthase homologen Proteins gibt, konntedie Struktur noch nicht vollständig aufgeklärt werden. ZurLösung des Phasenproblems wird mit der Methode der multiplenanomalen Dispersion (MAD) jetzt versucht, die ersteKristallstruktur in dieser Enzymfamilie aufzuklären.

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Elimination of an intraarticular femoroacetabular impingement conflict. Creation of a pain-free, normal range of motion of the hip.

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We consider the inertially driven, time-dependent biaxial extensional motion of inviscid and viscous thinning liquid sheets. We present an analytic solution describing the base flow and examine its linear stability to varicose (symmetric) perturbations within the framework of a long-wave model where transient growth and long-time asymptotic stability are considered. The stability of the system is characterized in terms of the perturbation wavenumber, Weber number, and Reynolds number. We find that the isotropic nature of the base flow yields stability results that are identical for axisymmetric and general two-dimensional perturbations. Transient growth of short-wave perturbations at early to moderate times can have significant and lasting influence on the long-time sheet thickness. For finite Reynolds numbers, a radially expanding sheet is weakly unstable with bounded growth of all perturbations, whereas in the inviscid and Stokes flow limits sheets are unstable to perturbations in the short-wave limit.