The present disclosure generally relates to a method for integrity testing filters, such as liquid sterilizing grade filters.
High purity filtration of aqueous media, such as in the fields of biotechnology, chemistry, electronics, pharmaceuticals, and the food and beverage industries requires the use of sophisticated filter modules that are not only capable of a high degree of separation, but that will tend to prevent contamination of the environment, of the medium to be filtered, and of the resulting filtrate. This is designed to prevent unwanted, often dangerous organisms, such as bacteria or viruses, as well as environmental contaminants, such as dust, dirt, and the like from entering into the process stream and end product. To ensure that the sterility and/or retention capability of the porous material responsible for the filtration is not compromised, integrity testing is a fundamental requirement of critical process filtration applications. For example, FDA guidelines recommend integrity testing of filter modules prior to use and after filtration. Typically this testing is initially performed after steam sterilization to ensure that the filter is not damaged; accordingly, care must be taken to ensure that sterility of the filter, and thus the filtrate, is not compromised. Post-processing, the filter integrity test is performed again in situ to detect whether the filter was compromised during use. This information can be used to alert operators to a potential problem immediately after processing, and to quickly take corrective action. Further, FDA guidelines require that integrity testing documentation be included with batch product records.
There are a variety of methods of integrity testing to detect the presence of oversized pores or defects that can compromise the retention capability of porous materials, including the particle challenge test, the liquid-liquid porometry test, the diffusion test, the bubble point test, the gas-liquid diffusion test and diffusion tests measuring tracer components. Some of these tests, such as the particle challenge test, are destructive and therefore cannot be used as a pre-use test. Gas-liquid diffusion tests often lack sensitivity for detecting small defects, due to the inherent background noise in these tests. Liquid-liquid porometry and bubble point tests are useful for ensuring that a membrane with the proper nominal pore size is installed, but lack sensitivity for identifying small numbers of small defects.
Also known in the art is the binary gas test, where two gases of differing permeabilities are driven through the liquid layer of a wetted filter. This test allows for improved defect detection sensitivity compared to the single gas diffusion test and other integrity tests. A sweep flow of the binary gas pair on the upstream side of the membrane to maintain a constant composition on the upstream (inlet) side of the filter is used. A pressure differential between the upstream and downstream side of the filter is established by elevating the pressure of the inlet gas. The concentration of the gases on the downstream (permeate) side of the filter (enriched in the faster permeating gas) is then measured, and this measured value is compared to a known expected value from an integral filter. A deviation from the expected value is indicative of a defect in the filter being tested.
The binary gas test typically uses CO2 and C2F6 as the binary gas pair and water as the wetting liquid. The use of CO2 is advantageous in that it is highly permeable in water, resulting in a high flow rate through the wetted filter and a rapid measurement of the permeate concentration. However, CO2 is costly, particularly in a binary gas mixture with the preferred gas pair C2F6. Furthermore, the use of this binary gas pair is undesirable in view of the greenhouse gas implications, since the permeate and sweep gases are emitted or must be captured to prevent emission to the ambient air.
Other binary gas pairs, such as O2 and N2, also have been used. This pair is convenient in that they are present in air, is low cost and is environmentally friendly. At room temperature, oxygen permeates through water about twice as fast as nitrogen. However, the permeability of oxygen in water is about 30 times slower than carbon dioxide, adding to the time necessary to complete the test in comparison to when CO2 is one of the binary gases.
The low permeate flow rate with air means that an extended time is required to flush the volume downstream of the filter and the volume up to and including the volume in the gas composition analyzer. Flushing is required to ensure that the measured composition is not compromised by mixing with any gas existing in the downstream volume prior to the start of the test. The long test time is in itself problematic but also introduces a secondary problem in that the liquid contained in the filter will tend to dry out due to liquid evaporation from both the upstream and downstream sides of the filter. If the pores dry out, the test can no longer be performed.
In light of the above, a need exists for an integrity test method for filters that allows for the use of relatively slow permeate gas pairs, but does not require excessive test times and minimizes or eliminates the risk that the filter will dry out during the test.
The problems of the prior art are addressed by the embodiments disclosed herein, which include a method of integrity testing porous materials that is non-destructive to the material being tested. In certain embodiments, the method includes humidifying the inlet gas stream to minimize or prevent the porous material from drying out. In certain embodiments, the inlet gas stream includes at least two gases, wherein one of the gases has a different permeability than the other in the liquid (e.g., water) used to wet the porous material. In certain embodiments, the at least two gases include oxygen and nitrogen. In certain embodiments, the inlet gas stream is air. In certain embodiments, the permeate gas stream is subjected to a driving force such as reduced pressure to increase the flow of gases and reduce test time. In some embodiments, multiple porous materials can be integrity tested at the same time, such as by manifolding a plurality of them together. The integrity test is capable of detecting the presence of oversized pores or defects that can compromise the retention capability of the porous material. In certain embodiments, the porous material is a sterilizing grade filter.
In some embodiments, a system for integrity testing a porous material is provided, the system comprising a gas stream source comprising at least first and second gases humidified with a wetting liquid at or near the saturation vapor pressure of the wetting liquid; a housing comprising a porous material wetted with a wetting liquid, the porous material having a first and second surface, the housing being in fluid communication with the gas stream source; a vacuum pump or the like in communication with the housing; and an analyzer for measuring the concentration of at least one of the first and second gases in a permeate stream exiting the second surface of the porous material.
In certain embodiments, the integrity test is rapid, sensitive, non-destructive, inexpensive, not deleterious to the environment, and easy to carry out. It provides a reliable assessment of the integrity of the porous material or element, while maintaining a highly stable integrity signal, and enabling the use of low permeability but otherwise very convenient and low cost gases in conjunction with a sensitive binary gas test method.
For a better understanding of the present disclosure, reference is made to the accompanying drawings, which are incorporated herein by reference and in which:
Before describing the embodiments in further detail, a number of terms will be defined.
As used herein, the singular forms “a”, “an”, and “the” include, plural referents unless the context clearly dictates otherwise.
The expression “integral” as used herein when referring to porous materials such as a porous single layer or porous membrane, porous multilayers, or a plurality of porous membranes, means a non-defective porous material.
The expression “non-integral” or as used herein when referring to porous materials such as a porous single layer or porous membrane, porous multilayers, and a plurality of porous membranes means a defective porous material. Non-limiting examples of defects in a porous layer or membrane include, but are not limited to, oversized pores, improper bonding (e.g., delamination or separation) between a plurality of porous layers or membranes that are bonded together to form a multilayer element, and defects on the porous layer or porous membrane.
The expression “porous material”, as used herein, may include, but is not limited to, one or more porous membranes, sheets, rods, discs, tubes, layers, filters, filter elements, filtration media, containers, cylinders, cassettes, cartridges, columns, chips, beads, plates, monoliths, hollow fibers, and combinations thereof. The porous materials may be pleated, flat, spirally wound, and combinations thereof. It may be a single layered or multilayered membrane device. The membrane may be symmetric or asymmetric. The porous material may be contained in a housing, which may have an inlet and an outlet. It may be used for filtration of unwanted materials including contaminants such as infectious organisms and viruses, as well as environmental toxins and pollutants. The porous material may be comprised of any suitable material, including, but not limited to polyether sulfone, polyamide, e.g., nylon, cellulose, polytetrafluoroethylene, polysulfone, polyester, polyvinylidene fluoride, polypropylene, a fluorocarbon, e.g. poly (tetrafluoroethylene-co-perfluoro(alkyl vinyl ether)), poly carbonate, polyethylene, glass fiber, polycarbonate, ceramic, and metals.
Embodiments disclosed herein include a method for integrity testing porous materials, including porous single layer materials, porous materials having a multi-layered configuration, porous membranes and filters. The porous material may be in a housing providing a feed or inlet side and a permeate or outlet side. In certain embodiments, a plurality of gases, such as a low-cost binary gas pair, such as oxygen and nitrogen, available via compressed air, are used as the inlet gas to perform the test. In certain embodiments, the porous material is wetted (i.e., the pores in the material are filled) with a liquid, such as water, and a first surface of the wetted porous material to be tested is contacted, under pressure, with the humidified gas. In certain embodiments, the identity of the liquid used to humidify the gas is the same as the liquid used to wet the porous material. The concentration of at least one of the gases near a second surface of the porous material (e.g., in a permeate stream of the porous material) is measured. In some embodiments, the measured concentration is compared to a predetermined concentration to determine if the porous material is integral or non-integral. In some embodiments, the predetermined concentration is the concentration expected from an integral porous material or device. In certain embodiments, a vacuum is applied to the permeate stream to accelerate the flushing of the downstream volume of the device containing the porous material. Suitable vacuum levels include any downstream pressure below atmospheric. In certain embodiments, a downstream pressure between about 1 psia and 5 psia is suitable.
Suitable amounts of each gas are not particularly limited. The gases should have different permeation rates through the liquid used to wet the porous material. The ratio of faster permeating gas to slower permeating gas in the gas mixture is influenced by a number of factors, including the ease of composition measurement, gas flow rate through the membrane, and economic considerations. In the case of air, the composition is fixed by ambient conditions. The composition of air on a dry basis is 20.95% O2, 78.09% N2, 0.93% Ar, 0.04% CO2, and trace levels of other gases.
The predetermined concentration may be the concentration of gas calculated to diffuse through an integral (i.e., non-defective), wetted porous material at a given temperature and pressure, or may be an actual concentration of gas that diffused through an integral wetted porous material at a given temperature and pressure.
In certain embodiments, the porous material is wetted with a liquid (a “wetting liquid”) by saturating the porous material with the liquid. Suitable liquids include water, isopropyl alcohol and mixtures of isopropyl alcohol and water. Other liquids also could be used but may not be ideal due to cost and/or convenience.
In another embodiment an apparatus or system for assessing the integrity of a porous material is provided, the apparatus comprising first and second gas sources; a gas inlet pressure regulator; a humidifier; a porous material sample; and a gas analyzer. Suitable humidifiers include any device which promotes transfer of a liquid into a gas. Although the term “humidity” refers specifically to the amount of water vapor contained in a gas (usually air), the humidifiers suitable for use herein need not be limited to this; they more generally include any device which promotes the vaporization of a liquid so that it is at its saturated vapor pressure. Suitable analyzers depend on the component or components being measured, and include oxygen analyzers for measuring oxygen concentration, mass spectrometers and Fourier Transform Infrared (FTIR) spectrometers. The apparatus may optionally further comprise a vacuum pump or the like for applying a vacuum to the permeate stream of the porous material sample. Where more than one porous material is manifolded together, the apparatus may include suitable valving for sequentially directing respective permeate streams to the gas analyzer. Alternatively or in addition, more than one gas analyzer can be used.
Suitable temperatures for carrying out the integrity test range from about 4° C. to about 40° C., preferably between about 22-24° C. Suitable feed pressures range from about 15 psia to about 100 psia, preferably about 40-70 psia.
Air was used as the inlet composition, at a feed pressure of 50 psig and a temperature of 22-24° C. The permeate pressure was 0 psig, and the sweep ratio (the flow rate of retentate (non-permeate) gas to the flow rate of permeate gas) was 500. As seen in
In order to accelerate the flushing of the downstream volume, in certain embodiments a driving force such as a vacuum can be applied to the downstream side of the porous material as illustrated in
In accordance with certain embodiments, multiple filter devices can be manifolded together and the permeate streams can be sampled sequentially, as exemplified in
Since multiple filters are equilibrating simultaneously, the average test time for each filter is reduced. For example, if 60 minutes is required for the permeate concentration exiting a device to reach a steady state value, then if five devices are equilibrated simultaneously, and 10 minutes are needed to sample each device, then with a single oxygen analyzer, 110 minutes would be needed to test the five devices, or an average of 22 minutes per device, compared to 70 minutes per device if tested sequentially as single devices. This embodiment relies on maintaining a stable permeate concentration for an extended period of time (no drying of the porous material), which is assured only with a humidified inlet stream.
The present disclosure is not to be limited in scope by the specific embodiments described herein. Indeed, other various embodiments of and modifications to the present disclosure, in addition to those described herein, will be apparent to those of ordinary skill in the art from the foregoing description and accompanying drawings. Thus, such other embodiments and modifications are intended to fall within the scope of the present disclosure. Furthermore, although the present disclosure has been described herein in the context of a particular implementation in a particular environment for a particular purpose, those of ordinary skill in the art will recognize that its usefulness is not limited thereto and that the present disclosure may be beneficially implemented in any number of environments for any number of purposes. Accordingly, the claims set forth below should be construed in view of the full breadth and spirit of the present disclosure as described herein.
This application claims priority of U.S. Provisional Application Ser. No. 62/257,830 filed on Nov. 20, 2015, the disclosure of which is incorporated herein by reference in its entirety.
Filing Document | Filing Date | Country | Kind |
---|---|---|---|
PCT/US2016/051268 | 9/12/2016 | WO | 00 |
Publishing Document | Publishing Date | Country | Kind |
---|---|---|---|
WO2017/087057 | 5/26/2017 | WO | A |
Number | Name | Date | Kind |
---|---|---|---|
5480554 | Degen et al. | Jan 1996 | A |
6119506 | Gibson et al. | Sep 2000 | A |
6214231 | Cote et al. | Apr 2001 | B1 |
6228271 | Cote | May 2001 | B1 |
6983504 | Grummert et al. | Jan 2006 | B2 |
7594425 | Lewnard et al. | Sep 2009 | B2 |
7972515 | Mangum et al. | Jul 2011 | B1 |
7982481 | Dehmel et al. | Jul 2011 | B2 |
8571296 | Jons | Oct 2013 | B2 |
20010020416 | Yoshikawa | Sep 2001 | A1 |
20020117232 | Gisper-Sauch et al. | Aug 2002 | A1 |
20040123646 | Echigo et al. | Jul 2004 | A1 |
20050229681 | Yamaguchi et al. | Oct 2005 | A1 |
20070089489 | Lewnard et al. | Apr 2007 | A1 |
20070120275 | Liu | May 2007 | A1 |
20080110243 | Burke | May 2008 | A1 |
20110138936 | Collins et al. | Jun 2011 | A1 |
20120080375 | Scheu et al. | Apr 2012 | A1 |
20130019658 | Hao et al. | Jan 2013 | A1 |
20130158933 | Huang et al. | Jun 2013 | A1 |
20130192346 | Steele | Aug 2013 | A1 |
20130234723 | Behrens et al. | Sep 2013 | A1 |
20140298893 | Laubstein et al. | Oct 2014 | A1 |
Number | Date | Country |
---|---|---|
2257151 | Aug 2005 | CA |
102049199 | May 2011 | CN |
102313691 | Jan 2012 | CN |
102435224 | May 2012 | CN |
102492663 | Jun 2012 | CN |
4215585 | Nov 1993 | DE |
19726379 | Jan 1999 | DE |
20009001 | Aug 2000 | DE |
19918419 | Oct 2000 | DE |
10116335 | Oct 2002 | DE |
102011111050 | Feb 2013 | DE |
102012216772 | Mar 2014 | DE |
0139202 | May 1985 | EP |
0518250 | Dec 1992 | EP |
0582822 | Feb 1994 | EP |
0831318 | Mar 1998 | EP |
0909210 | Dec 2000 | EP |
1210298 | Apr 2003 | EP |
1775015 | Apr 2007 | EP |
1897605 | Mar 2008 | EP |
1925356 | May 2008 | EP |
2238461 | Oct 2010 | EP |
2436653 | Apr 2012 | EP |
2490794 | Aug 2012 | EP |
2567750 | Mar 2013 | EP |
2668489 | Dec 2013 | EP |
2909904 | Jun 2008 | FR |
2004-219407 | Aug 2004 | JP |
2007-108178 | Apr 2007 | JP |
2014-504732 | Feb 2014 | JP |
2011-0127011 | Nov 2011 | KR |
1020491 | Oct 2003 | NL |
1021197 | Oct 2003 | NL |
9319356 | Sep 1993 | WO |
9322970 | Nov 1993 | WO |
9745193 | Dec 1997 | WO |
0050158 | Aug 2000 | WO |
0059615 | Oct 2000 | WO |
0116030 | Mar 2001 | WO |
0145829 | Jun 2001 | WO |
2009092694 | Jul 2009 | WO |
2011049790 | Apr 2011 | WO |
2012103124 | Aug 2012 | WO |
2017087057 | May 2017 | WO |
Entry |
---|
International Search Report and Written Opinion dated Jan. 10, 2017 in corresponding PCT application No. PCT/US2016/051268. |
International Preliminary Report on Patentability dated May 22, 2018 in corresponding PCT application No. PCT/US2016/051268. |
Belanger et al., “Use of Pressure-Hold Test for Sterilizing Filter Membrane Integrity in Radiopharmaceutical Manufacturing”, Nuclear Medicine and Biology, vol. 36, Iss.8, pp. 955-959, 2009. |
Giglia et al., “New Binary Gas Integrity Test Improves Membrane Quality Assurance”, BioPharm International, vol. 24, Iss.4, four pages, 2011. |
Giglia et al, “High Sensitivity Binary Gas Integrity Test for Membrane Filters”, Journal of Membrane Science, vol. 323, Iss.1, pp. 60-66, 2008. |
Kent et al., “An Evaluation of Membrane Integrity Monitoring Methods for Micro- and Ultrafiltration Systems”, American Water Works Association, WQTC Conference, pp. 1-10, 2005. |
Lieberman, “Characterization of Particles in Liquid Suspension”, Tappi Journal, Filter Evaluation, vol. 71, Iss.6, pp. 105-113, 1988. |
Meyer, “Filter Testing: Parallel Integrity Testing of Small Venting Filters”, Filtration & Separation, vol. 46, Iss.6, pp. 22-24, 2009. |
Meltzer, “Microfiltration: Diffusive Airflow Integrity Testing Revisited”, Ultrapure Water, vol. 6, Iss.9, pp. 41-44, 1989. |
Number | Date | Country | |
---|---|---|---|
20180257039 A1 | Sep 2018 | US |
Number | Date | Country | |
---|---|---|---|
62257830 | Nov 2015 | US |