Aims: This study compared the effectiveness of solifenacin succinate (SS) versus percutaneous tibial nerve stimulation (PTNS) in women with overactive bladder syndrome (OABS). Methods: A randomized controlled crossover study of 40 women with OABS was performed. Patients were randomized into two groups. In group A, patients received SS and then PTNS. In group B, patients underwent PTNS and then SS. Voiding diaries, quality of life surveys and patient perception of intensity of urgency questionnaire were performed before and after each treatment. The global impression of improvement questionnaire was performed at the end of the study. Results: A reduction in the number of daily micturitions, episodes of nocturia and urge incontinence were found with both SS and PTNS in all groups, but PTNS showed a greater effectiveness than SS. There was an increase in voided volume in all groups with both SS and PTNS, but patients treated with PTNS had a greater increase. PTNS showed greater effectiveness in patient perception of urgency and quality of life. Conclusion: This study demonstrates the effectiveness of SS and PTNS In women with overactive bladder symptoms. However, greater improvements were found with PTNS.
This work aims at investigating the possibility of a wireless sensor network powered by an energy harvesting technology, such as a microbial fuel cell (MFC). An MFC is a bioreactor that transforms energy stored in chemical bonds of organic compounds into electrical energy. This process takes place through catalytic reactions of microorganisms under anaerobic conditions. An anode chamber together with a cathode chamber composes a conventional MFC reactor. The protons generated in the anode chamber are then transferred into the cathode chamber through a proton exchange membrane (PEM). A possible option is to use the soil itself as the membrane. In this case, we are referring to, more properly, a terrestrial microbial fuel cell (TMFC). This research examines the sustainability of a wireless sensor network powered by TMFC for land monitoring and precision agriculture. Acting on several factors, such as pH, temperature, humidity and type of soil used, we obtained minimum performance requirements in terms of the output power of the TMFC. In order to identify some of the different network node configurations and to compare the resulting performance, we investigated the energy consumption of the core components of a node, e.g., the transceiver and microcontroller, looking for the best performance.
OPEN ACCESSSustainability 2014, 6 7264
This paper aims to show different techniques for identifying brownfields and for monitoring based on remote sensing. If brownfields are associated with urban wastes such as the demolition of buildings, dangerous materials or contaminants will be involved with them. Hazard and health risks increase, so the administration policy needs to detect, at an early stage, dangerous materials or contaminants and to manage the cleaning and recovery of these land areas. A detailed classification of the land and the identification of these typologies of brownfields can be carried out by means of hyperspectral remote sensing using the airborne MIVIS (Multispectral Infrared and Visible Imaging Spectrometer) sensor of the Laboratory of CNR (LARA). Thanks to MIVIS, we can detect many different materials. The subsequent integration of data into GIS allows identification of brownfields through our specific software tools that determine the contours of objects and evaluate the statistical parameters of the processed images. Moreover, other GIS tools correlate data in order to evaluate the extent and derivative parameters of the same brownfields. When brownfields are associated with urban or sub-urban abandoned industrial properties or a land with neglected vegetation, i.e. with the evident characteristic of land abandoned or under-used; then the previous method is useless. These brownfields are missing specific hazardous substances or contaminants and buildings and are generally in good condition. For these last cases, an alternative process should be implemented. A higher geometric resolution than MIVIS should be used, putting in evidence small objects in the soil and so IKONOS or QuickBird satellite imagery are required. In this case, brownfield identification will be carried out by means of object-oriented algorithms and the mutual relationship between them.
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