4 resultados para Cyanotoxins, Blue-green algae, UV-LEDs, Photospheres™, water treatment

em DigitalCommons@The Texas Medical Center


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In Halobacterium salinarum phototaxis is mediated by the visual pigment-like photoreceptors sensory rhodopsin I (SRI) and II (SRII). SRI is a receptor for attractant orange and repellent UV-blue light, and SRII is a receptor for repellent blue-green light, and transmit signals through the membrane-bound transducer proteins HtrI and HtrII, respectively. ^ The primary sequences of HtrI and HtrII predict 2 transmembrane helices (TM1 and TM2) followed by a hydrophilic cytoplasmic domain. HtrII shows an additional large periplasmic domain for chemotactic ligand binding. The cytoplasmic regions are homologous to the adaptation and signaling domains of eubacterial chemotaxis receptors and, like their eubacterial homologs, modulate the transfer of phosphate groups from the histidine protein kinase CheA to the response regulator CheY that in turn controls flagellar motor rotation and the cell's swimming behavior. HtrII and Htrl are dimeric proteins which were predicted to contain carboxylmethylation sites in a 4-helix bundle in their cytoplasmic regions, like eubacterial chemotaxis receptors. ^ The phototaxis transducers of H. salinarum have provided a model for studying receptor/tranducer interaction, adaptation in sensory systems, and the role of membrane molecular complexes in signal transduction. ^ Interaction between the transducer HtrI and the photoreceptor SRI was explored by creating six deletion constructs of HtrI, with progressively shorter cytoplasmic domains. This study confirmed a putative chaperone-like function of HtrI, facilitating membrane insertion or stability of the SRI protein, a phenomenon previously observed in the laboratory, and identified the smallest HtrI fragment containing interaction sites for both the chaperone-like function and SRI photocycle control. The active fragment consisted of the N-terminal 147 residues of the 536-residue HtrI protein, a portion of the molecule predicted to contain the two transmembrane helices and the first ∼20% of the cytoplasmic portion of the protein. ^ Phototaxis and chemotaxis sensory systems adapt to stimuli, thereby signaling only in response to changes in environmental conditions. Observations made in our and in other laboratories and homologies between the halobacterial transducers with the chemoreceptors of enteric bacteria anticipated a role for methylation in adaptation to chemo- and photostimuli. By site directed mutagenesis we identified the methylation sites to be the glutamate pairs E265–E266 in HtrI and E513–E514 in HtrII. Cells containing the unmethylatable transducers are still able to perform phototaxis and adapt to light stimuli. By pulse-chase analysis we found that methanol production from carboxylmethyl group hydrolysis occurs upon specific photo stimulation of unmethylatable HtrI and HtrII and is due to turnover of methyl groups on other transducers. We demonstrated that the turnover in wild-type H. salinarum cells that follows a positive stimulus is CheY-dependent. The CheY-feedback pathway does not require the stimulated transducer to be methylatable and operates globally on other transducers present in the cell. ^ Assembly of signaling molecules into architecturally defined complexes is considered essential in transmission of the signals. The spectroscopic characteristics of SRI were exploited to study the stoichiometric composition in the phototaxis complex SRI-HtrI. A molar ratio of 2.1 HtrI: 1 SRI was obtained, suggesting that only 1 SRI binding site is occupied on the HtrI homodimer. We used gold-immunoelectron microscopy and light fluorescence microscopy to investigate the structural organization and the distribution of other halobacterial transducers. We detected clusters of transducers, usually near the cell's poles, providing a ultrastructural basis for the global effects and intertransducer communication we observe. ^

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The occurrence of waste pharmaceuticals has been identified and well documented in water sources throughout North America and Europe. Many studies have been conducted which identify the occurrence of various pharmaceutical compounds in these waters. This project is an extensive review of the documented evidence of this occurrence published in the scientific literature. This review was performed to determine if this occurrence has a significant impact on the environment and public health. This project and review found that pharmaceuticals such as sex hormone drugs, antibiotic drugs and antineoplastic/cytostatic agents as well as their metabolites have been found to occur in water sources throughout the United States at levels high enough to have noticeable impacts on human health and the environment. It was determined that the primary sources of this occurrence of pharmaceuticals were waste water effluent and solid wastes from sewage treatment plants, pharmaceutical manufacturing plants, healthcare and biomedical research facilities, as well as runoff from veterinary medicine applications (including aquaculture). ^ In addition, current public policies of US governmental agencies such as the Environmental Protection Agency (EPA), Food and Drug Administration (FDA), and Drug Enforcement Agency (DEA) have been evaluated to see if they are doing a sufficient job at controlling this issue. Specific recommendations for developing these EPA, FDA, and DEA policies have been made to mitigate, prevent, or eliminate this issue.^ Other possible interventions such as implementing engineering controls were also evaluated in order to mitigate, prevent and eliminate this issue. These engineering controls include implementing improved current treatment technologies such as the advancement and improvement of waste water treatment processes utilized by conventional sewage treatment and pharmaceutical manufacturing plants. In addition, administrative controls such as the use of “green chemistry” in drug synthesis and design were also explored and evaluated as possible alternatives to mitigate, prevent, or eliminate this issue. Specific recommendations for incorporating these engineering and administrative controls into the applicable EPA, FDA, and DEA policies have also been made.^

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Developing countries are heavily burdened by limited access to safe drinking water and subsequent water-related diseases. Numerous water treatment interventions combat this public health crisis, encompassing both traditional and less-common methods. Of these, water disinfection serves as an important means to provide safe drinking water. Existing literature discusses a wide range of traditional treatment options and encourages the use of multi-barrier approaches including coagulation-flocculation, filtration, and disinfection. Most sources do not delve into approaches specifically appropriate for developing countries, nor do they exclusively examine water disinfection methods.^ The objective of this review is to focus on an extensive range of chemical, physio-chemical, and physical water disinfection techniques to provide a compilation, description and evaluation of options available. Such an objective provides further understanding and knowledge to better inform water treatment interventions and explores alternate means of water disinfection appropriate for developing countries. Appropriateness for developing countries corresponds to the effectiveness of an available, easy to use disinfection technique at providing safe drinking water at a low cost.^ Among chemical disinfectants, SWS sodium hypochlorite solution is preferred over sodium hypochlorite bleach due to consistent concentrations. Tablet forms are highly recommended chemical disinfectants because they are effective and very easy to use, but also because they are stable. Examples include sodium dichloroisocyanurate, calcium hypochlorite, and chlorine dioxide, which vary in cost depending on location and availability. Among physio-chemical disinfection options, electrolysis which produces mixed oxidants (MIOX) provides a highly effective disinfection option with a higher upfront cost but very low cost over the long term. Among physical disinfection options, solar disinfection (SODIS) applications are effective, but they treat only a fixed volume of water at a time. They come with higher initial costs but very low on-going costs. Additional effective disinfection techniques may be suitable depending on the location, availability and cost.^

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The objectives of this research were: to determine the contribution of algae to commonly run water quality variables, to evaluate waste pond micoorganisms' capacity to degrade and accumulate ten EPA priority pollutants, and to determine the environmental fate of those compounds in a laboratory