COMPORTAMENTO DO NONI À SALINIDADE DA ÁGUA DE IRRIGAÇÃO EM SOLO COM BIOFERTILIZANTE BOVINO1.

O excesso de sais no solo e em águas utilizadas para irrigação podem provocar perdas significativas de crescimento e de produção em plantas cultivadas. Dentre algumas alternativas para redução dos efeitos negativos dos sais às plantas em áreas cultivadas, a utilização do biofertilizante fermentado vem sendo explorada no cultivo de hortaliças e frutíferas irrigadas com água salina. Nesse sentido, o trabalho teve como objetivo avaliar o comportamento do noni à salinidade da água de irrigação em substrato sem e com biofertilizante bovino. Os tratamentos foram distribuídos em blocos ao acaso, com quatro repetições, utilizando o arranjo fatorial 5 x 2, correspondente a cinco níveis de condutividade elétrica da água de irrigação (0,5; 1,5; 3,0; 4,5; 6,0 dS m-1), em substratos com e sem biofertilizante bovino. Foram avaliados: altura de plantas, diâmetro do caule, número de folhas, área foliar, matéria seca da parte aérea e consumo hídrico. Todas as variáveis avaliadas foram influenciadas negativamente pelo incremento de sais na água de irrigação, mas sempre com menor intensidade nos tratamentos com biofertilizante bovino. O biofertilizante não elimina, mas atenua os efeitos negativos dos sais às plantas de noni.

Relações hídricas em cultivares de beterraba em diferentes níveis de salinidade do solo

The excess of salts in the soil can directly affect the development and yield of the plants, therefore, studies on water relationships of crops in such conditions are necessary to prevent or solve the problem. The study was conducted in a greenhouse at Universidade Estadual Paulista, Department of Agricultural Engineering, Botucatu, Brazil. The statistical design used was randomized blocks with four replications, consisting of five levels of soil salinity (1.0, 3.0, 6.0, 9.0, 12.0 dS m-1), two cultivars of sugar beet (Early Wonder and Itapuã) and two types of management of fertigation, totaling in all 80 plots. Measurements of water content of the leaves, diffuse resistance to water vapor, transpiration, leaf area and the water consumption of crop were determined. There was a decrease according to increasing salinity for the analysed physiological parameters in the Early Wonder variety while for the Itapuã variety a gradual increase was observed up to a salinity of 6 dS m-1. The water consumption by plants showed a reduction with increase of soil salinity for the two varieties.

Processamento de farinha de resíduo de polpa de amora-preta (Rubus sp.) e avaliação de biocompostos

Pós-graduação em Biociências - FCLAS

Cassava wastewater as carbon source for the polyhydroxybutyrate production by Azotobacter vinelandii CCT 2841

Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)

Imobilização da enzima álcool desidrogenase em suportes alginato-quitosana e glioxil-agarose

Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)

Fontes e doses de fósforo na presença e ausência de composto orgânico no estado nutricional e na produtividade da cana-de-açúcar

Pós-graduação em Agronomia (Ciência do Solo) - FCAV

Determinação de chumbo por análise voltamétrica de pulso diferencial por redissolução anódica em regiões de falhas geológicas com emissão de radônio e filhos de radônio no município de Presidente Prudente

Pós-graduação em Química - IBILCE

Persistência de cepas de Escherichia coli genérica e de Stec não-O157 em solos agricultáveis

Pós-graduação em Microbiologia Agropecuária - FCAV

Produção da cultura da beterraba irrigada com água salina.,

The use of low quality water for agriculture should be performed with care to avoiding excessive accumulation of salts in the soil so not to harm crop development. In order to evaluate the performance of beets under the infl uence of low water quality, an experiment was conducted in a greenhouse of the Department of Agricultural Engineering, Universidade Estadual Paulista in Botucatu, Brazil, from April to July 2012. We used the beet (Beta vulgaris L.) in a completely randomized design with 6 treatments and 5 replications, totaling 30 plots. Treatments consisted of NaCl solutions at different concentrations (2.0, 3.0, 4.0, 5.0 and 6.0 dS m-1) plus a control treatment corresponding to water with no additional salt and electrical conductivity of roughly 0.26 dS m-1. Variables evaluated were total production, commercial production, plant height, number of plants and root diameter. Production of the beet crop was affected by the increasing salinity of irrigation water, characterized by reduced root production of the beets. Total and commercial production showed reductions of 8.82 and 12.2% in accordance with the unit increase of salinity.

Synthesis and Photodynamic Effect of New Highly Photostable Decacationically Armed [60]- and [70]Fullerene Decaiodide Monoadducts To Target Pathogenic Bacteria and Cancer Cells

Novel water-soluble decacationically armed C-60 and C-70 decaiodide monoadducts, C-60- and C-70[>M(C3N6+C3)(2)], were synthesized, characterized, and applied as photosensitizers and potential nano-PDT agents against pathogenic bacteria and cancer cells. A high number of cationic charges per fullerene cage and H-bonding moieties were designed for rapid binding to the anionic residues displayed on the outer parts of bacterial cell walls. In the presence of a high number of electron-donating iodide anions as parts of quaternary ammonium salts in the arm region, we found that C-70[>M(C3N6+C3)(2)] produced more HO center dot than C-60[>M(C3N6+C3)(2)], in addition to O-1(2). This finding offers an explanation of the preferential killing of Gram-positive and Gram-negative bacteria by C-60[>M(C3N6+C3)(2)] and C-70[>M(C3N6+C3)(2)], respectively. The hypothesis is that O-1(2) can diffuse more easily into porous cell walls of Gram-positive bacteria to reach sensitive sites, while the less permeable Gram-negative bacterial cell wall needs the more reactive HO center dot to cause real damage.

New insights on reaction pathway selectivity promoted by crown ether phase-transfer catalysis: Model ab initio calculations of nucleophilic fluorination

Crown ethers have the ability of solubilizing inorganic salts in apolar solvents and to promote chemical reactions by phase-transfer catalysis. However, details on how crown ethers catalyze ionic S(N)2 reactions and control selectivity are not well understood. In this work, we have used high level theoretical calculations to shed light on the details of phase-transfer catalysis mechanism of KF reaction with alkyl halides promoted by 18-crown-6. A complete analysis of the of the model reaction between KF(18-crown-6) and ethyl bromide reveals that the calculations can accurately predict the product ratio and the overall kinetics. Our results point out the importance of the K* ion and of the crown ether ring in determining product selectivity. While the K* ion favors the S(N)2 over the E2 anti pathway, the crown ether ring favors the S(N)2 over E2 syn route. The combination effects lead to a predicted 94% for the S(N)2 pathway in excellent agreement with the experimental value of 92%. A detailed analysis of the overall mechanism of the reaction under phase-transfer conditions also reveals that the KBr product generated in the nucleophilic fluorination acts as an inhibitor of the 18-crown-6 catalyst and it is responsible for the observed slow reaction rate. (C) 2012 Elsevier B.V. All rights reserved.

High Viscosity of Imidazolium Ionic Liquids with the Hydrogen Sulfate Anion: A Raman Spectroscopy Study

Ionic liquids based on 1-alkyl-3-methylimidazolium cations and the hydrogen sulfate (or bisulfate) anion, HSO4-, are much more viscous than ionic liquids with alkyl sulfates, RSO4-. The structural origin of the high viscosity of HSO4- ionic liquids is unraveled from detailed comparison of the anion Raman bands in 1-ethyl-3-methylimidazolium hydrogen sulfate and 1-butyl-3-methylimidazolium hydrogen sulfate with available data for simple HSO(4)(-) salts in crystalline phase, molten phase, and aqueous solution. Two Raman bands at 1046 and 1010 cm(-1) have been assigned as symmetric stretching modes nu(s)(S = O) of HSO4-, the latter being characteristic of chains of hydrogen-bonded anions. The intensity of this component increases in the supercooled liquid phase. For comparison purposes, Raman spectra of 1-ethyl-3-methylimidazolium ethyl sulfate and 1-butyl-3-methylimidazolium methyl sulfate have been also obtained. There is no indication of difference in the strength of hydrogen bond interactions of imidazolium cations with HSO4- or RSO4- anions. Raman spectra at high pressures, up to 2.6 GPa, are also discussed. Raman spectroscopy provides evidence that hydrogen-bonded anions resulting in anion-anion interaction is the reason for the high viscosity of imidazolium ionic liquids with HSO4-. If the ionic liquid is exposed to moisture, these structures are disrupted upon absorption of water from the atmosphere.

Effects of moisture content on structural and dielectric properties of cassava starch films

In this work, it was evaluated the effect of moisture content on the structural and dielectric properties of cassava starch films by means of Fourier Transform infrared spectroscopy (FTIR), impedancimetric, and gravimetric analysis. The film samples were equilibrated in hermetically sealed desiccators, containing different saturated salts in water in order to promote activity of water between 0.11 and 0.85. The position and amplitude of the peaks in the fingerprint region of the FTIR spectra were changed due to the modifications in the interactions between the polymeric chains and water molecules. These effects may be related to the formation of semi-crystalline regions in the film structure. The dielectric properties of the films were also strongly dependent on the moisture content, showing a non-linear and a linear region, which was attributed to the domain of bound and free water in the film, respectively. The gravimetric analyzes showed the typical sigmoidal behavior, attributed to the way the water interacts with the biopolymer. Finally, the flexibility of the films increased with water content increasing.

Bioremediation of PAHs - Limitations and soultions

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.

Formtreue organische Makrocyclen mit polarem Innenraum

Zusammenfassung Die Arbeit beschreibt die Synthese und Eigenschaften von formtreuen organischen Makrocyclen mit intraannularen polaren Gruppen. Dabei wurden zunächst entsprechende bifunktionalisierte Acetylenbausteine (Halbringe) hergestellt, welche anschließend in einer oxidativen Glaser-Eglington Kupplung zu den Makrocyclen umgesetzt wurden.Am Anfang wurden Sulfonat-funktionalisierte Makrocyclen untersucht. Diese ließen sich mittels der Templatmethode in hohen Ausbeuten synthetisieren. Nach der Abspaltung des Templatbausteins, der gleichzeitig als Schutzgruppe für die Sulfonsäure diente, erhielt man den entsprechenden Makrocyclus als Tetra-n-butylammonium-Salz. Vor dem Hintergrund ionenleitfähige Materialien zu erhalten, wurde anschließend das organische Kation durch anorganische Kationen (z.B. Li+, Na+) ausgetauscht. Dies führte jedoch zur Bildung unlöslicher Produkte, die sich nicht eindeutig charakterisierten ließen.Ein anderer Ansatz zu löslichen Makrocyclen mit polarem Innenraum zu gelangen war die Synthese eines Dipeptid-funktionalisierten Makrocyclus. Dies geschah im Hinblick auf die eventuelle Eignung der Makrocyclen als Rezeptormoleküle für Gäste biologischen Ursprungs. Dabei ließen sich die entsprechenden Dipeptid-funktionalisierten Halbringe auf einfache Weise darstellen, jedoch trat bei der anschließenden Glaser-Kupplung, wahrscheinlich bedingt durch den hohen molaren Überschuß an Kupfersalzen, als Hauptreaktion die Abspaltung des Peptidrests auf. Daher wurde sich nun der Carbonsäuregruppe als polaren Baustein im Inneren der Ringe zugewandt. Diese sollten eine anschließende Peptidankupplung zulassen.Es wurden vier verschiedene Makrocyclen mit intraannularen Carboxylatgruppen synthetisiert. Auch hier waren die Makrocyclen in Form ihrer Methylester noch gut, in Form der Säuren oder deren Salze oftmals nur noch sehr gering löslich. Um die Löslichkeit zu verbessern, wurde dabei die Polaritätsverteilung am Ring (polarer Innenraum, unpolarer Außenraum) durch das Anbringen von löslichkeits-vermittelnden Gruppen zum Teil aufgegeben. Dabei hat sich gezeigt, daß es erst durch die Verwendung von verzweigten (S)-Methylbutoxy-Gruppen innerhalb des Rings oder langen Alkoxyketten außerhalb des Rings möglich war, zu löslichen Systemen zu gelangen. Im ersten Fall ist es zum ersten Mal gelungen, einen löslichen Makrocyclus mit zwei freien intra-annnularen Carbonsäuregruppen zu erhalten. Durch die Optimierung der Syntheseroute ist es nunmehr möglich, den Ring im Grammmaßstab herzustellen. Außerdem wurden als Testreaktion beide Säuregruppen mit Methylamin zum Säureamid vollständig umgesetzt. Somit wurde ein System entwickelt, an das sich in Zukunft beliebige Aminosäuren an den Ring anbinden lassen sollten. Zusätzlich sollte sich die Chiralität der (S)-Methylbutoxygruppen auf das Erkennen von chiralen Gästen auswirken.Im zweiten Fall wurden durch das Anbringen von vier Tris(hexadecyloxy)-benzol- oder Tris(dodecyloxy)-benzol- Gruppen an der Peripherie der Ringe nach Hydrolyse der Methylestergruppen ebenfalls lösliche, Carboxylat-funktionalisierte Makrocyclen erhalten. Eine eingehende Untersuchung der Methylester-geschützten Ringe ergab, daß diese beim Schmelzen das Auftreten einer thermotropen flüssigkristallinen Phase zeigen. Die Natur der Mesophase konnte mittels Polarisations-Lichtmikroskopie sowie Röntgenbeugungsmethoden eindeutig als kolumnar-schiefwinklig (colob) charakterisiert werden. Hierbei ist zu bemerken, daß bei ähnlichen Makrocyclen, die über keinen polar gefüllten Innenraum verfügen, keine Mesophase auftritt. Das bedeutet, daß die Raumerfüllung im Inneren der Makrocyclen, bedingt durch die polaren Gruppen, zur Ausbildung einer flüssigkristallinen Phase unbedingt notwendig ist.