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Applied and Environmental Microbiology, October 2008, p. 6470-6472, Vol. 74, No. 20
0099-2240/08/$08.00+0 doi:10.1128/AEM.00552-08
Copyright © 2008, American Society for Microbiology. All Rights Reserved.

Department of Morphology and Embryology, Section of Cell Biology and Molecular Genetics, School of Medicine,1 Center of Biotechnology, University of Ferrara, Via Fossato di Mortara 64/B, 44100 Ferrara, Italy,2 GVS SpA, 40069 Zola Predosa, Italy3
Received 7 March 2008/ Accepted 10 August 2008
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LPS are formed by three fractions, known as lipid A, core oligosaccharide, and O-antigen (6, 7). Since LPS are partially phosphorylated, the P group confers the net negative charge.
Removing undesirable endotoxins from aqueous solutions is an important aim in the pharmaceutical industry and in clinical practice. Indeed, intravenous (i.v.) therapy is an integral part of modern patient care and is used in the clinical management of the treatment of more than a quarter of hospitalized patients. Unfortunately, i.v. systems also provide a direct route for microorganisms to enter the bloodstream (4). The introduction of a 0.22-µm filter membrane into the i.v. line prevents inadvertent microbial (bacterial, fungal, and yeast) contamination in i.v. fluids from reaching the patient (3, 8). The removal of bacterial endotoxins from liquids is often difficult. The conventional heat sterilization of liquids and filtration with microporous membrane filters, which kill or remove whole bacterial cells, do not eliminate bacterial endotoxins (10, 11). Endotoxins can be eliminated by heating for long periods at elevated temperatures, while the depyrogenation of heat-sensitive biological materials is not feasible. Endotoxins can be removed using ion exchange resins, activated carbon (5), or asbestos-containing filters (9).
Due to the difficulty in removing endotoxins by conventional methods (10), the production of innovative filters able to retain endotoxins is an important goal for the pharmaceutical industry and for medicine. A new filter, known as Speedflow Positive and equipped with a HI-FLO polyethersulfone (PES) 0.2-µm-pore-size positively charged membrane that electrostatically attracts and/or retains endotoxins, has been produced by GVS SpA (Zola Predosa, Italy) and is referred to hereinafter as filter A. This filter is a modification of a standard filter, known as Speedflow (GVS) and referred to hereinafter as filter C, which guarantees superior flow rate performance and protection against contamination. These new-generation filters (both A and C) are formed by two opposing layers of hydrophilic membranes in a small package; it guarantees mechanical resistance with pump applications, total safety from air embolism, the elimination of large globules in liquids with lipids, and the removal of drug precipitates.
In this study, the two GVS filters A and C were comparatively assayed with two additional filters, B and D, purchased from Pall SpA, Milano, Italy. Filter B is an adult-size 10-cm2 positively charged PES membrane with 0.2-µm pores, and filter D is an adult-size 10-cm2 standard PES membrane with 0.2-µm pores.
The endotoxin retention assay was carried out with an apparatus which consisted of a test filter, sterile tubing sets, Luer lock outlet connections, a peristaltic pump, and nonpyrogenic glass reservoirs. The depyrogenation cycle was set at 200°C for 4 h.
Pyrotell Limulus amoebocyte lysate (LAL) lot no. S05-398 (Associates of Cape Cod [ACC], MA), with a sensitivity of 0.03 endotoxin units (EU)/ml, was used for the gel clot method LAL test. The control standard endotoxin (CSE [lot no. 100; ACC]) was from Escherichia coli strain 0113. The accuracy of the gel clot LAL test was established by the range of endotoxin concentrations determined as indicated by the manufacturer (ACC). However, the exact endotoxin concentrations are not known. Nevertheless, the data obtained in our experiments are consistent with the purpose of our work. The reproducibility of the results obtained with the gel clot LAL test was ensured. There was no variability in the results; indeed, we obtained the same data by repeating the experiments 20 times. Results from four representative experiments are shown in Table 1.
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TABLE 1. Endotoxin measurements by the LAL testa
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CSE challenge solution (CS) was prepared by dissolving lyophilized CSE in nonpyrogenic water to yield a concentration of 1 EU/ml in 10 liters. To confirm the concentration, a sample of CS was collected and evaluated by the LAL test. The endotoxin retention test was carried out using the following apparatus: a silicon tube edge, attached to the filter, was inserted into the 10-liter reservoir with the 1-EU/ml CSE solution and threaded through an infusion pump; the polyvinyl chloride tube edge terminated in a nonpyrogenic vessel (Fig. 1). The pump was set up to start at 80 ml/h. The first filtrate fluid (FF) was collected at the beginning of the assay, while subsequent samples of FF and CS which had not passed through the filter were collected after 8, 24, 48, 72, and 96 h of filtration and then tested for endotoxin concentrations by the gel clot method LAL test. All test results were deemed to be valid as the CS yielded the same endotoxin concentration measurement (1 EU/ml) in all the experiments. The endotoxin measurements performed on the filtrates from filters A and B consistently indicated that the amounts of endotoxin which had passed through the filters during the infusion experiment time (96 h) were less than 0.03 EU/ml. On the contrary, the filtrates from filters C and D showed amounts of endotoxin similar to that in the CS (1 EU/ml). From these assay results, we can infer that only filters equipped with a positively charged membrane, filters A and B, were able to retain the endotoxin. Indeed, filters with a standard membrane, filters C and D, did not retain the LPS. This result obtained with purified E. coli CSE (ACC) extends the work by Schindler and Dinarello (10). Gerba and Hou (2) demonstrated that increasing the net positive charge on filters results in the enhancement of endotoxin retention. Nevertheless, Gerba and Hou (2) obtained good results with depth filters but not with membrane filters.
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FIG. 1. Apparatus used to carry out the test: an infusion pump was used to test each tubing set and filter, with a 1-EU/ml CSE solution. PVC, polyvinyl chloride.
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We thank Georgia Gili for her excellent assistance in revising the manuscript.
Published ahead of print on 22 August 2008. ![]()
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