Reverse Osmosis-Based Treatment of Radioactive Liquid Wastes Generated in Hospital Facility and in Steel Industry

2008 ◽  
pp. 919-931
Author(s):  
M Sancho ◽  
J Arnal ◽  
G Verd√∫ ◽  
J Lora
Desalination ◽  
2003 ◽  
Vol 154 (1) ◽  
pp. 27-33 ◽  
Author(s):  
J.M. Arnal ◽  
M. Sancho ◽  
G. Verdú ◽  
J.M. Campayo ◽  
J.I. Villaescusa

2021 ◽  
Vol 8 (5) ◽  
pp. 449-464
Author(s):  
María Sancho ◽  
◽  
José Miguel Arnal ◽  
Gumersindo Verdú-Martín ◽  
Cristina Trull-Hernandis ◽  
...  

<abstract> <p>Radioactive liquid wastes are produced at hospitals from diagnostic and therapeutic applications of radionuclides. The most usual management of these wastes is temporary storage at the hospital for radioactivity decay and, then, discharge into sewage if not other pollutants are present in waste, always after authorization of the corresponding institution. In some cases, radioactive wastes have other hazards, such as chemical or biological ones, which can be more dangerous than radiological hazard, and do not allow direct discharge into sewage in spite of decaying activity below the clearance level. Therefore, these wastes have to be treated and condition before discharge in spite of activity decay below discharge limit. This is the case of liquid wastes from radioimmunoassay (RIA), a laboratory technique that allows to determine human substances in very low concentrations (below 10<sup>-12</sup> g/mL), like hormones, using <sup>125</sup>I as radionuclide. This study summarizes the usual management of radioactive liquid wastes from hospitals, including conventional and recent treatments applied. Furthermore, based on experimental results obtained with real RIA wastes, this work exposes a proposal of treatment with ultrafiltration and reverse osmosis membranes, and determines the most suitable application of this treatment according to radiological and operational considerations.</p> </abstract>


2016 ◽  
Vol 2016 ◽  
pp. 1-9 ◽  
Author(s):  
Hanaa M. Ali ◽  
Hanaa Gadallah ◽  
Sahar S. Ali ◽  
Rania Sabry ◽  
A. G. Gadallah

This paper was focused on the investigation of a forward osmosis- (FO-) reverse osmosis (RO) hybrid process to cotreat seawater and impaired water from steel industry. By using this hybrid process, seawater can be diluted before desalination, hence reducing the energy cost of desalination, and simultaneously contaminants present in the impaired water are prevented from migrating into the product water through the FO and RO membranes. The main objective of this work was to investigate on pilot-scale system the performance of the combined FO pretreatment and RO desalination hybrid system and specifically its effects on membrane fouling and overall solute rejection. Firstly, optimization of the pilot-scale FO process to obtain the most suitable and stable operating conditions for practical application was investigated. Secondly, pilot-scale RO process performance as a posttreatment to FO process was evaluated in terms of water flux and rejection. The results indicated that the salinity of seawater reduced from 35000 to 13000 mg/L after 3 hrs using FO system, while after 6 hrs it approached 10000 mg/L. Finally, FO/RO system was tested on continuous operation for 15 hrs and it was demonstrated that no pollutant was detected neither in draw solution nor in RO permeate after the end of operating time.


Desalination ◽  
2006 ◽  
Vol 201 (1-3) ◽  
pp. 207-215 ◽  
Author(s):  
M. Sancho ◽  
J.M. Arnal ◽  
G. Verdú ◽  
J. Lora ◽  
J.I. Villaescusa

Desalination ◽  
2003 ◽  
Vol 154 (1) ◽  
pp. 35-42 ◽  
Author(s):  
J.M. Arnal ◽  
M. Sancho ◽  
G. Verdú ◽  
J.M. Campayo ◽  
J.M. Gozálvez

2016 ◽  
Vol 130 ◽  
pp. 103-115 ◽  
Author(s):  
Valentina Colla ◽  
Teresa Annunziata Branca ◽  
Felice Rosito ◽  
Carmelo Lucca ◽  
Beatriz Padilla Vivas ◽  
...  

Author(s):  
H. K. Plummer ◽  
E. Eichen ◽  
C. D. Melvin

Much of the work reported in the literature on cellulose acetate reverse osmosis membranes has raised new and important questions with regard to the dense or “active” layer of these membranes. Several thickness values and structures have been attributed to the dense layer. To ensure the correct interpretation of the cellulose acetate structure thirteen different preparative techniques have been used in this investigation. These thirteen methods included various combinations of water substitution, freeze drying, freeze sectioning, fracturing, embedding, and microtomy techniques with both transmission and scanning electron microscope observations.It was observed that several factors can cause a distortion of the structure during sample preparation. The most obvious problem of water removal can cause swelling, shrinking, and folds. Improper removal of embedding materials, when used, can cause a loss of electron image contrast and, or structure which could hinder interpretation.


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