Manufacturers of filtration devices often offer small scale sizing tools for initial evaluation of process streams and for estimating membrane area requirements for the full scale process. Ideally, small scale devices should contain a minimum of membrane area or filtration media to save test fluid while also scaling linearly with their corresponding large scale devices. However, variability in the performance of small scale devices adds uncertainty to the scale-up requirements, resulting in potentially excessive sizing to guard against the possibility that the tested small scale device(s) represented the low end of the performance distribution.
In the case of microfiltration membrane filters, for example, there are many factors that influence membrane performance, including the pore size distribution, the membrane chemistry, membrane thickness, membrane porosity, and others. While membrane manufacturing processes are designed to control all of these factors to maximize uniformity and consistency, there inevitably will be some distribution within normal manufacturing conditions for all of these variables. This membrane variability limits device-to-device performance consistency and therefore limits the precision to which large scale performance can be predicted from small scale performance.
The performance of either large scale samples or small scale filtration devices is often used to estimate the sizing requirements of large scale devices. The use of small scale devices for sizing provides an obvious economic advantage. For example, in sterile filtration of biological fluids, 47 mm or 25 mm membrane discs offer a convenient format for evaluating performance against the discs to large scale membrane devices (e.g., cartridges containing tens to thousands of times more area). For accurate scale-up, the membrane in the small scale device must be representative of the membrane in the large scale devices. However, as in any manufacturing process, there is a finite tolerance in acceptable performance from one lot of membranes to another. The membrane in a scaling device could originate from anywhere within the acceptable performance range. Accordingly, when estimating the required sizing of full scale devices, the variability in membrane performance must be accounted for, necessitating the use of liberal safety factors in scaling estimates.
This can be illustrated by considering a hypothetical distribution of membrane performances as shown in
Usf=(Fh/Sl)/(Fl/Sh)=(Fh/Fl)*(Sh/Sl) (1)
where Fh is the full scale high end potential performance, Fl is the full scale low end potential performance, Sh is the scaling device high end potential performance, and Sl is the scaling device low end potential performance.
It therefore would be desirable to reduce the range of scaling device performance in order to lower large scale device requirements and save costs.
The problems of the prior art have been overcome by the present invention, which provides a method of reducing the range of scaling device performance uncertainty. In certain embodiments, scaling device performance uncertainty is reduced, thereby reducing the scaling safety factor, by specifying a narrow range or subset of the set of all qualified manufactured membranes or filtration media for installation into scaling devices. In certain embodiments, the scalability factor is reduced by determining where within the performance distribution a particular membrane lies, and adjusting the scaling factor accordingly. Reducing scaling uncertainty results in significant cost savings, realized, for example, by a reduction in the scale-up sizing requirements.
Membrane manufacturing processes inherently result in some variability in membrane properties even though materials and process conditions are kept as constant as possible. As a result, procedures have been instituted to classify or “rate” each batch or roll of membranes after manufacture, based on performance. For example, water permeability and throughput capacity tests are often carried out such as by constructing membrane devices using membranes from a given batch, measuring water permeability, and challenging the devices with a solution containing particles of a selected size and concentration to plug the membrane pores. Throughput capacity (volume filtered) within a specified time period, such as 10 minutes, or some flow reduction amount, such as 70% flow reduction, are measured, and relative capacity values are obtained. The membranes from the given batch are then performance rated based upon the results obtained. The performance of filtration media may also be similarly characterized. Filtration media is material that actively separates solids from a solution and/or binds select materials in solution. Types of filter media include: non-woven fabrics, activated carbon, activated clay, cellulose, ceramic, cotton, diatomaceous earth, glass fiber, ion exchange resins, metals, minerals, paper, nylon, sand, synthetic fiber, Teflon, polyethersulfone, polyester, polypropylene, polytetrafluoroethelyne, polyvinylidene fluoride, polyvinylidene chloride, and polysulfone.
In certain embodiments of carrying out the methods disclosed herein, each batch of membranes or filtration media produced is characterized by performance, and a performance distribution is established. From that distribution, a small subset is selected for installation into scaling devices. By specifying only a narrow range of the distribution for scaling devices, the uncertainty in scaling from small scale to large scale devices (which by definition can contain any qualified membrane or filtration media) is minimized.
For example, if only the middle third of the distribution is selected for small scale devices, as illustrated in
In certain embodiments, the scalability safety factor can be minimized by determining where, within the performance distribution, the small scale device lies (using either a surrogate or actual performance qualification test, for example), and then adjusting the scaling factor to account for the specific portion of the distribution that the scaling device came from. In this approach, any membrane can be used in scaling devices. Information about membrane performance is collected and the information is then provided with the finished device. When the scaling device is evaluated, this membrane performance data is used in determining the scaling factor. For example, using the hypothetical distribution in
Usf=Fh/Fl (2)
The scaling factor uncertainty ratio in this case becomes 1.3/0.7, or 1.86, which represents a 46% reduction compared to uninformed membrane selection.
A key performance parameter of sterilizing grade membrane filters is water permeability, which relates to the productivity of the device. Water permeability is measured by supplying water to the membrane, maintaining a pressure difference across the membrane, and measuring the water flow rate. Permeability is calculated according to the formula:
Lp=Q/(A*ΔP)
where Lp is water permeability, A is the membrane area, and ΔP is the pressure difference across the membrane. Water permeability is commonly expressed in units of L/(m2-hr-psi) or LMH/psi.
The water permeability was measured on a representative set of pleated cartridges each containing about 0.5 m2 of polyethersulfone membrane with a nominal pore size of 0.2 μm. A plot of the distribution is shown in
From the water permeability distribution of Example 1, a single membrane that had been characterized for water permeability was selected from the entire population of membranes. Since the water permeability of this membrane was known, equation 2 was applicable and the scaling factor uncertainty ratio was 1300/1000=1.3, represents a 23% improvement in scaling factor uncertainty compared to the prior art.
This application is a continuation of U.S. patent application Ser. No. 12/848,435 filed Aug. 2, 2010, which claims priority of U.S. Provisional Application Ser. No. 61/274,142 filed Aug. 13, 2009, the disclosures of which are incorporated herein by reference.
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Number | Date | Country | |
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20130140224 A1 | Jun 2013 | US |
Number | Date | Country | |
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61274142 | Aug 2009 | US |
Number | Date | Country | |
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Parent | 12848435 | Aug 2010 | US |
Child | 13754928 | US |