Patent Application
20150292995
The present disclosure relates to methods, kits, systems and devices for processing samples for microorganism analysis.
The determination of the absence or presence of coliform bacteria (as well as other microorganisms and contaminants) is one of the basic analyses to assess the sanitary quality of water. The presence of fecal coliforms in a sample is a primary indication of fecal contamination of the sample water and may indicate the possible presence of other pathogenic organisms. Methods for enumerating microbes in water samples are well known and many have been standardized. Currently available standard methods for enumerating bacteria in water samples are generally expensive and require multiple steps, sophisticated instrumentation and highly trained personnel.
Membrane filtration is a commonly utilized technique to obtain a direct count of microorganisms present in low concentrations in large volume samples of water. The operational requirements for most membrane filtration techniques (vacuum manifolds) or centrifugation (powered equipment) make them unsuitable for on-site applications. In addition, filtration of large volumes by use of mechanical means (via pistons or plungers) or manually applied pressure is very labor intensive due to the pressure required to force the sample through membranes having pore sizes small enough to isolate bacteria (0.22 to 0.45 microns). Thus, there is a need for simple, non-labor intensive, inexpensive, portable sample acquisition methods for processing large sample volumes.
Disclosed herein is a method for isolating microorganisms from a sample, the sample including sample matrix and microorganisms, the method including the steps of: providing a receptacle, the receptacle configured to allow filtering of the sample and to reversibly contain the sample and a concentration agent; adding the sample to the receptacle, wherein a microorganism-bound composition will be formed in the receptacle, the microorganism-bound composition having concentration agent-bound microorganisms and sample matrix; and filtering the microorganism-bound composition through a filter to collect the concentration agent-bound microorganisms on the filter, wherein the filter has an average pore size that is greater than the average size of the microorganisms.
Disclosed herein is a kit that includes concentration agent; and a system for isolating microorganisms from a sample, the system including: a receptacle configured to allow filtering of the sample and to reversibly contain the sample and a concentration agent; and a filter, the filter having a first surface and a second surface and comprising pores having an average pore size that is larger than the average size of the microorganisms.
Disclosed herein is a system for isolating microorganisms from a sample, the sample having sample matrix and microorganisms, the system including a liner configured to afford contact of a concentration agent and the sample, to provide a microorganism-bound composition that includes concentration agent-bound microorganisms and sample matrix; a filter, the filter having a first surface and a second surface and comprising pores having an average pore size that is larger than the average size of the microorganisms; a filter support configured to contact the first surface of the filter and afford contact of the microorganism-bound composition with the second surface of the filter, wherein the liner and filter support are configured to afford filtration of the microorganism-bound composition through the filter in order to collect the concentration agent-bound microorganisms on the second surface of the filter.
Disclosed herein is a kit that includes concentration agent; and a system for isolating microorganisms from a sample, the system including: a liner configured to afford contact of the concentration agent and the sample, providing a microorganism-bound composition that includes concentration agent-bound microorganisms and sample matrix; a filter, the filter having a first surface and a second surface and having pores having an average pore size that is larger than the average size of the microorganisms; a filter support configured to contact the first surface of the filter and afford contact of the microorganism-bound composition with the second surface of the filter, wherein the liner and filter support are configured to afford filtration of the microorganism-bound composition through the filter in order to collect the concentration agent having bound microorganisms on the second surface of the filter.
Disclosed herein is a method for isolating microorganisms from a sample, the sample having sample matrix and microorganisms, the method including the steps of: placing a liner having an opening in a container to form a receptacle assembly, the container configured to at least partially receive the liner; adding the sample to the liner to form a microorganism-bound composition in the liner, the microorganism-bound composition including concentration agent-bound microorganisms and sample matrix; placing a filter over at least a portion of the opening of the liner; placing a filter support on the filter to form a filter assembly, the filter assembly including the liner, the container, the filter and the filter support; inverting the filter assembly; and filtering the microorganism-bound composition through the filter to collect the concentration agent-bound microorganisms on the filter.
The disclosure may be more completely understood in consideration of the following detailed description of various embodiments of the disclosure in connection with the accompanying drawings, in which:
The figures are not necessarily to scale. Like numbers used in the figures refer to like components. However, it will be understood that the use of a number to refer to a component in a given figure is not intended to limit the component in another figure labeled with the same number.
In the following description, reference is made to the accompanying drawings that form a part hereof, and in which are shown by way of illustration several specific embodiments. It is to be understood that other embodiments are contemplated and may be made without departing from the scope or spirit of the present disclosure. The following detailed description, therefore, is not to be taken in a limiting sense.
All scientific and technical terms used herein have meanings commonly used in the art unless otherwise specified. The definitions provided herein are to facilitate understanding of certain terms used frequently herein and are not meant to limit the scope of the present disclosure.
Unless otherwise indicated, all numbers expressing feature sizes, amounts, and physical properties used in the specification and claims are to be understood as being modified in all instances by the term “about.” Accordingly, unless indicated to the contrary, the numerical parameters set forth in the foregoing specification and attached claims are approximations that can vary depending upon the desired properties sought to be obtained by those skilled in the art utilizing the teachings disclosed herein.
The recitation of numerical ranges by endpoints includes all numbers subsumed within that range (e.g. 1 to 5 includes 1, 1.5, 2, 2.75, 3, 3.80, 4, and 5) and any range within that range.
As used in this specification and the appended claims, the singular forms “a”, “an”, and “the” encompass embodiments having plural referents, unless the content clearly dictates otherwise. As used in this specification and the appended claims, the term “or” is generally employed in its sense including “and/or” unless the content clearly dictates otherwise.
Disclosed herein are methods, systems, kits and devices for processing samples. The methods, systems, kits and devices can offer advantages in processing samples in that they provide a quick, easy, simple and relatively inexpensive way to prepare water samples (for example) for microbiological analyses. Further advantage is provided by the ability to accomplish universal sample concentration options from large volumes for detecting low levels of bacteria, spores or viruses. The methods and devices can significantly reduce back pressure and leakage issues that are often associated with filtering for microbiological analyses (because of the very small pore size filters that are usually required). The methods and devices can be quick, simple, portable and require no expensive equipment or highly skilled technician. When large pore size filters (e.g. at least about 10 μm or greater) are utilized, coliform enumeration can be done directly in commercially available culture films, such as 3M™ PETRIFILM™ E. Coli/Coliform Count Plates (3M Company, St. Paul Minn.). When utilized with disposable receptacles, only the disposable portion of the system contacts the sample, thereby eliminating the need to clean and sterilize the device prior to the next use.
An exemplary method is depicted in
The first step in the exemplary method, step 110 includes providing a receptacle. The step of providing a receptacle can include merely obtaining a receptacle or making a receptacle. For example, a receptacle could be purchased for use in the method, a receptacle could be modified from a purchased article, or a receptacle could be made based on the teaching provided herein, for example.
Generally, a receptacle that can be utilized herein is configured to at least reversibly contain the sample and allow filtering of the sample. Numerous types and configurations of receptacles could be utilized in the method and kits disclosed herein. A receptacle can be a single opening receptacle or a multiple opening receptacle. A single opening receptacle can be configured to afford addition of the sample (and other optional components) and filtering of the sample from the same opening. A multiple opening receptacle can be configured to afford addition of the sample (and other optional components) via one opening and filtering of the sample via a second opening. In an embodiment, a multiple opening receptacle includes two openings and is referred to herein as a double opening receptacle. In an embodiment, the application can dictate the type of receptacle to be utilized.
A receptacle that can be utilized herein can be formed of a variety of materials including, but not limited to, polymeric materials, metals (e.g., aluminum, stainless steel, etc.), ceramics, glasses, and combinations thereof. Examples of polymeric materials can include, but are not limited to, polyolefins (e.g., polyethylene, polypropylene, combinations thereof, etc.), polycarbonate, acrylics, polystyrene, high density polyethylene (HDPE), polypropylene, other suitable polymeric materials capable of forming a freestanding and/or self-supporting container, or a combination thereof. In an embodiment, the receptacle can be made of materials which are relatively inexpensive and can therefore be disposable. The receptacle can be translucent (or even transparent), or opaque, and can be any suitable size, depending on the type, amount and size of source to be analyzed. In an embodiment, the application can dictate the amount of sample to be utilized. In an embodiment, the receptacle can have a capacity of any useful volume, for example, a capacity from about 5 mL to about 1000 mL. In an embodiment, the receptacle can have a capacity from about 5 mL to about 500 mL. In an embodiment, the receptacle can have a capacity from about 5 mL to about 250 mL. In an embodiment, the receptacle can have a capacity from about 10 mL to about 250 mL. For example, in some embodiments, the receptacle can have a capacity of 10 mL, 50 mL, 100 mL, 250 mL, or larger for example.
A receptacle that can be utilized herein is configured to at least reversibly contain the sample. Reversibly contain the sample means that the receptacle can contain the sample (and other components) but the sample or at least a portion of the sample can be removed from the receptacle by for example, filtering. The size of receptacle to be utilized can therefore depend at least in part on the size of the sample to be collected. In an embodiment, the sample can be processed (i.e. combined with concentration agent) in a different container and can then be filtered utilizing the receptacle. In an embodiment, the receptacle can contain a larger volume or smaller volume than the sample to be collected. The receptacle can be chosen based on the sample size to be collected, or the sample size to be collected can be chosen based on the receptacle size.
A receptacle that can be utilized herein is configured to allow the sample to be filtered. Generally, this implies that the receptacle is configured to be operably coupled with a filter. In an embodiment, the receptacle can contain or can be configured to be coupled with an element that supports a filter. In an embodiment, this element can be referred to as a filter support. A filter support can function to maintain the filter in operable communication with the receptacle. Exemplary types of filter supports can offer support across substantially the entire surface area of the filter or less than the entire surface area of the filter. The combination of the filter, the receptacle and the filter support can be referred to herein as a filter assembly. In an embodiment with a disposable liner and a container that holds the disposable liner (discussed in greater detail below), the combination of the filter, the container, the liner and the filter support can be referred to as a filter assembly.
Specific exemplary types of receptacles can be found in the following commonly assigned Patent Applications, the disclosures of which are incorporated herein by reference: U.S. Patent Application No. 60/989,180, entitled “SYSTEM AND METHOD FOR PREPARING AND ANALYZING SAMPLES”, filed on Nov. 20, 2007; PCT Publication No. WO2009/067503, entitled “SAMPLE PREPARATION FOR ENVIRONMENTAL SAMPLING”; PCT Patent Publication No. WO2007/137257, entitled “SYSTEM AND METHOD FOR PREPARING SAMPLES”; U.S. Patent Application No. 60/989,175, entitled “SYSTEM AND METHOD FOR PREPARING AND DELIVERING SAMPLES”, filed on Nov. 20, 2007; and PCT Publication No. WO2008/150779, entitled “DEVICES AND PROCESSES FOR COLLECTING AND CONCENTRATING SAMPLES FOR MICROBIOLOGICAL ANALYSIS”. Further details related to some of the receptacle types disclosed in these applications will be discussed below.
The second step in the exemplary method depicted in
Generally, a sample contains sample matrix and microorganisms. The term sample matrix generally refers to everything within a sample besides the microorganisms. For example, the sample matrix in a water sample includes water, the dissolved material in the water sample and the undissolved material (with the exception of the microorganisms).
The term “microorganism” is generally used to refer to any prokaryotic or eukaryotic microscopic organism, including without limitation, one or more of bacteria (e.g., motile or vegetative, Gram positive or Gram negative), viruses (e.g., Norovirus, Norwalk virus, Rotavirus, Adenovirus, DNA viruses, RNA viruses, enveloped, non-enveloped, human immunodeficiency virus (HIV), human Papillomavirus (HPV), etc.), bacterial spores or endospores, algae, fungi (e.g., yeast, filamentous fungi, fungal spores), prions, mycoplasmas, and protozoa. In some cases, the microorganisms of particular interest are those that are pathogenic, and the term “pathogen” is used to refer to any pathogenic microorganism. Examples of pathogens can include, but are not limited to, members of the family Enterobacteriaceae, or members of the family Micrococaceae, or the genera Staphylococcus spp., Streptococcus, spp., Pseudomonas spp., Enterococcus spp., Salmonella spp., Legionella spp., Shigella spp., Yersinia spp., Enterobacter spp., Escherichia spp., Bacillus spp., Listeria spp., Campylobacter spp., Acinetobacter spp., Vibrio spp., Clostridium spp., and Corynebacteria spp. Particular examples of pathogens can include, but are not limited to, Escherichia coli including enterohemorrhagic E. coli e.g., serotype 0157:H7, Pseudomonas aeruginosa, Bacillus cereus, Bacillus anthracis, Salmonella enteritidis, Salmonella typhimurium, Listeria monocytogenes, Clostridium botulinum, Clostridium perfringens, Staphylococcus aureus, methicillin-resistant Staphylococcus aureus, Campylobacter jejuni, Yersinia enterocolitica, Vibrio vulnificus, Clostridium difficile, vancomycin-resistant Enterococcus, and Enterobacter sakazakii. Environmental factors that may affect the growth of a microorganism can include the presence or absence of nutrients, pH, moisture content, oxidation-reduction potential, antimicrobial compounds, temperature, atmospheric gas composition and biological structures or barriers.
The amount of sample added to the receptacle can depend at least in part on the size and configuration of the receptacle, the amount of sample to be tested, other factors not discussed herein, or a combination thereof. In an embodiment, the amount of sample to be added to the receptacle can be between about 5 mL and 1000 mL. In an embodiment, the amount of sample to be added to the receptacle can be between about 5 mL and 500 mL. In an embodiment, the amount of sample to be added to the receptacle can be between about 10 mL and about 250 mL. Addition of the sample to the receptacle can be accomplished by any known method, including but not limited to, pouring or otherwise adding the sample (from another container) to the receptacle and immersing at least a portion of the receptacle into a larger portion of the sample (e.g. utilizing the receptacle to obtain a sample from a water supply for example).
One function of the receptacle is to allow the sample including microorganisms to interact with a concentration agent. A concentration agent is generally a material that microorganisms will bind to when the microorganisms are dispersed in a sample matrix. A concentration agent can be a particulate material or can be a dispersed material. Suitable particulate or dispersed materials include, for example, metal carbonates (e.g., calcium carbonate) and metal phosphates (e.g., hydroxyapatite). Binding of microorganisms by such concentration agents is generally not specific to any particular strain, species, or type of microorganism and therefore provides for the concentration of a general population of microorganisms in a sample. Specific strains of microorganisms can then be detected from among the captured microorganism population using any known detection method for example with strain-specific probes or with strain-specific culture media. Once the sample is combined with the concentration agent in the receptacle, a microorganism-bound composition is obtained. A microorganism-bound composition includes concentration agent-bound microorganisms and sample matrix.
One exemplary type of concentration agents include diatomaceous earth and surface-treated diatomaceous earth. Specific examples of such concentration agents can be found in commonly assigned PCT Patent Publication No. WO2009/046191, entitled “MICROORGANISMS CONCENTRATION PROCESS AND AGENT”, the disclosure of which is incorporated herein by reference. When dispersed or suspended in water systems, inorganic materials exhibit surface charges that are characteristic of the material and the pH of the water system. The potential across the material-water interface is called the “zeta potential,” which can be calculated from electrophoretic mobilities (that is, from the rates at which the particles of material travel between charged electrodes placed in the water system). In an embodiment, concentration agents can have zeta potentials that are at least somewhat more positive than that of untreated diatomaceous earth, and the concentration agents can be surprisingly significantly more effective than untreated diatomaceous earth in concentrating microorganisms such as bacteria, the surfaces of which generally tend to be negatively charged.
One exemplary type of concentration agent includes diatomaceous earth. Another exemplary type of concentration agent includes surface-treated diatomaceous earth. Exemplary surface treatment includes a surface modifier, such as titanium dioxide, fine-nanoscale gold or platinum, or a combination thereof Such surface treatments can be surprisingly more effective than untreated diatomaceous earth in concentrating microorganisms. The surface treatment can also further include a metal oxide selected from ferric oxide, zinc oxide, aluminum oxide, and the like, and combinations thereof In an embodiment, ferric oxide is utilized. Although noble metals such as gold have been known to exhibit antimicrobial characteristics, the gold-containing concentration agents can be effective not only in binding the microorganisms but also in leaving them viable for purposes of detection or assay.
Useful surface modifiers include fine-nanoscale gold; fine-nanoscale platinum; fine-nanoscale gold in combination with at least one metal oxide (for example, titanium dioxide, ferric oxide, or a combination thereof); titanium dioxide; titanium dioxide in combination with at least one other (that is, other than titanium dioxide) metal oxide; and the like; and combinations thereof. In an embodiment, surface modifiers such as fine-nanoscale gold; fine-nanoscale platinum; fine-nanoscale gold in combination with at least ferric oxide or titanium dioxide; titanium dioxide; titanium dioxide in combination with at least ferric oxide; or combinations thereof can be utilized.
In an embodiment surface modifiers such as the following can be utilized: fine-nanoscale gold; fine-nanoscale platinum; fine-nanoscale gold in combination with ferric oxide or titanium dioxide; titanium dioxide; titanium dioxide in combination with ferric oxide; and combinations thereof. In an embodiment, fine-nanoscale gold; fine-nanoscale gold in combination with ferric oxide or titanium dioxide; titanium dioxide in combination with ferric oxide; and combinations thereof can be utilized. Fine-nanoscale gold, fine-nanoscale gold in combination with ferric oxide or titanium dioxide, and combinations thereof can also be utilized in an embodiment.
Another exemplary type of concentration agent includes gamma-FeO(OH) (also known as lepidocrocite). Specific examples of such concentration agents can be found in commonly assigned PCT Patent Publication No. WO2009/046183, entitled “MICROORGANISM CONCENTRATION PROCESS”, the disclosure of which is incorporated herein by reference. Such concentration agents have been found to be surprisingly more effective than other iron-containing concentration agents in capturing gram-negative bacteria, which can be of great concern in regard to food- and water-borne illnesses and human bacterial infections. The concentration agents can further include (in addition to gamma-FeO(OH)) other components (for example, boehmite (α-AlO(OH)), clays, iron oxides, and silicon oxides). In embodiments where such other components are included, they generally do not significantly interfere with the intimate contact of the sample and the concentration agent.
Gamma-FeO(OH) is known and can be chemically synthesized by known methods (for example, by oxidation of ferrous hydroxide at neutral or slightly acidic pHs, as described for purposes of magnetic tape production in U.S. Pat. No. 4,729, 846 (Matsui et al.), the description of which is incorporated herein by reference). Gamma-FeO(OH) is also commercially available (for example, from Alfa Aesar, A Johnson Matthey Company, Ward Hill, Mass., and from Sigma-Aldrich Corporation, St. Louis, Mo.).
In an embodiment that utilized gamma-FeO(OH) as a concentration agent, the gamma-FeO(OH) is generally in the form of microparticles. In an embodiment, it is in the form of microparticles having particle sizes (largest dimension) in the range of about 3 micrometers (in other embodiments, about 5 micrometers; or about 10 micrometers) to about 100 micrometers (in other embodiments, about 80 micrometers; or about 50 micrometers; or about 35 micrometers; where any lower limit can be paired with any upper limit of the range). In an embodiment, the particles are agglomerates of smaller particles. The particles can include crystallites that are less than about 1 micrometer in size (in an embodiment, less than about 0.5 micrometer in size). The crystallites can be present as acicular crystallites, as raft-like structures comprising acicular crystallites, or as combinations of the acicular crystallites and raft-like structures.
In an embodiment, the concentration agents have a surface area as measured by the BET (Brunauer-Emmett-Teller) method (calculation of the surface area of solids by physical adsorption of nitrogen gas molecules) that is greater than about 25 square meters per gram (m2/g); in an embodiment greater than about 50 m2/g; and in another embodiment greater than about 75 m2/g.
An agglomerated form of the particles can provide the adsorptive capabilities of fine particle systems without the handling and other hazards often associated with fine particles. In addition, such agglomerate particles can settle readily in fluid and thus can provide rapid separation of microorganisms from a fluid phase (as well as allowing low back pressure when filtered).
Another exemplary type of concentration agents include metal silicates. Specific examples of such concentration agents can be found in commonly assigned PCT Patent Publication No. WO2009/085357, entitled “MICROORGANISM CONCENTRATION PROCESS”, the disclosure of which is incorporated herein by reference. Exemplary metal silicates can have a surface composition having a metal atom to silicon atom ratio of less than or equal to about 0.5 (in an embodiment, less than or equal to about 0.4; in another embodiment, less than or equal to about 0.3; in yet another embodiment, less than or equal to about 0.2), as determined by X-ray photoelectron spectroscopy (XPS). In an embodiment, the surface composition also includes at least about 10 average atomic percent carbon (in an embodiment, at least about 12 average atomic percent carbon; in yet another embodiment at least about 14 average atomic percent carbon), as determined by X-ray photoelectron spectroscopy (XPS). XPS is a technique that can determine the elemental composition of the outermost approximately 3 to 10 nanometers (nm) of a sample surface and that is sensitive to all elements in the periodic table except hydrogen and helium. XPS is a quantitative technique with detection limits for most elements in the 0.1 to 1 atomic percent concentration range. Exemplary surface composition assessment conditions for XPS can include a take-off angle of 90 degrees measured with respect to the sample surface with a solid angle of acceptance of ±10 degrees.
When dispersed or suspended in water systems, inorganic materials such as metal silicates exhibit surface charges that are characteristic of the material and the pH of the water system. The potential across the material-water interface is called the “zeta potential,” which can be calculated from electrophoretic mobilities (that is, from the rates at which the particles of material travel between charged electrodes placed in the water system). Exemplary concentration agents can have zeta potentials that are more negative than that of, for example, a common metal silicate such as ordinary talc. Yet the concentration agents are surprisingly more effective than talc in concentrating microorganisms such as bacteria, the surfaces of which generally tend to be negatively charged. In an embodiment, the concentration agents have a negative zeta potential at a pH of about 7 (in an embodiment, a Smoluchowski zeta potential in the range of about −9 millivolts to about −25 millivolts at a pH of about 7; in another embodiment, a Smoluchowski zeta potential in the range of about −10 millivolts to about −20 millivolts at a pH of about 7; in yet another embodiment a Smoluchowski zeta potential in the range of about −11 millivolts to about −15 millivolts at a pH of about 7).
Useful metal silicates include, but are not limited to, amorphous silicates of metals such as magnesium, calcium, zinc, aluminum, iron, titanium, and the like, and combinations thereof In an embodiment, magnesium, zinc, iron, titanium, or combinations thereof can be utilized. In yet another embodiment, magnesium is utilized. In an embodiment, amorphous metal silicates in at least partially fused particulate form can be utilized. In an embodiment, amorphous, spheroidized metal silicates can be utilized. In yet another embodiment, amorphous, spheroidized magnesium silicate can be utilized. Metal silicates are known and can be chemically synthesized by known methods or obtained through the mining and processing of raw ores that are naturally-occurring.
Some amorphous metal silicates are commercially available. For example, amorphous, spheroidized magnesium silicate is commercially available for use in cosmetic formulations (for example, as 3M Cosmetic Microspheres CM-111, available from 3M Company, St. Paul, Minn.).
In addition to amorphous metal silicates, the concentration agents can also include other materials including oxides of metals (for example, iron or titanium), crystalline metal silicates, other crystalline materials, and the like, provided that the concentration agents have the above-described surface compositions. In an embodiment, a concentration agent contains essentially no crystalline silica.
The concentration agents can be used in any form that is amenable to sample contact and microorganism capture. In an embodiment, the concentration agents are used in particulate form. In an embodiment, the concentration agent is in the form of microparticles. In an embodiment, the concentration agent is in the form of microparticles having a particle size in the range of about 1 micrometer (in an embodiment, about 2 micrometers) to about 100 micrometers (in an embodiment, about 50 micrometers; in another embodiment, about 25 micrometers; in yet another embodiment about 15 micrometers; where any lower limit can be paired with any upper limit of the range).
As exemplified in FIG. 1,the concentration agent can be added to the receptacle before the sample is added to the sample, path 141, or after the sample is added to the receptacle, path 143. The concentration agent can also be added substantially simultaneously with the addition of the sample. Furthermore, in an embodiment (not depicted in
The amount of concentration agent added to the receptacle can depend at least in part on the type of concentration agent utilized, the sample size, the receptacle type and size, sample mixing, the particular application, other factors not specifically discussed herein, or a combination thereof. The capture efficiency (the percent of microorganisms in the sample bound to concentration agent) can generally be increased by allowing increased time for the microorganism to come in contact with the concentration agent. The capture efficiency can also be increased by having a higher concentration of concentration agent, which decreases the mean diffusion distance a microorganism must travel to be captured, leading to a shorter incubation time. Therefore, as a generality, the more concentration agent added, the shorter incubation time necessary to capture the same amount of microorganisms.
In an embodiment, an appropriate amount of concentration agent can vary given the time necessary to wait for the microorganisms to be bound to the concentration agent (referred to as “capture time”). For example, for a capture time of 1 minute, 1000 mg of concentration agent per 10 mL of sample could be appropriate; for a capture time of 10 minutes, 100 mg of concentration agent per 10 mL of sample could be appropriate; and for a capture time of 60 minutes, 10 mg of concentration agent per 10 mL of sample could be appropriate. In an embodiment, from about 1 mg to about 100 mg of concentration agent per 10 mL of sample can be utilized. In an embodiment, from about 1 mg to about 50 mg of concentration agent per 10 mL of sample can be utilized. In an embodiment, from about 10 mg to about 25 mg of concentration agent per 10 mL of sample can be utilized. In an embodiment utilizing a metal silicate concentration agent for example, about 10 mg of a metal silicate concentration agent per 10 mL of sample can be utilized. In an embodiment utilizing a metal silicate concentration agent for example, about 25 mg of a metal silicate concentration agent per 10 mL of sample can be utilized.
As discussed above, once the sample and concentration agent is in the receptacle, a microorganism-bound composition (concentration agent-bound microorganisms and sample matrix) can be formed in the receptacle. The next step in the method, as depicted in
Exemplary filters having pore sizes greater than or equal to 1 micrometer are commercially available from numerous sources, examples of commercially available filters include, but are not limited to filters available from 3M CUNO, General Electric Company, Millipore, and Pall Corporation. Exemplary filter membranes with a 10 micrometer pore size are commercially available from GE Osmonics Lab Store (for example GE polycarbonate membrane) and Pall Corporation (MMM-Asymmetric Super-Micron membrane). Exemplary filters can also be prepared as disclosed in commonly assigned U.S. Pat. No. 7,553,417, entitled, “FUNCTIONALIZED SUBSTRATES”, and PCT Publication No. WO2009/048743, entitled “MICROPOROUS MEMBRANES HAVING A RELATIVELY LARGE AVERAGE PORE SIZE AND METHODS OF MAKING THE SAME”, the disclosures of which are incorporated herein by reference.
A filter can be described by its pore size (for example by its bubble point pore size). The bubble point pore size of a filter is generally the average of the largest size of the pores of the filter. In an embodiment, a filter having an average pore size that is greater than the average pore size of the microorganisms is utilized. In an embodiment, the filter can have an average pore size that is less than the average size of the concentration agent. The ability to utilize filters having these relatively large pore sizes offers significant advantages to methods as disclosed herein when compared with other methods for separating microorganisms from samples, such as water samples.
In an embodiment, the filter can have an average pore size that is at least about 1 micrometer (μm) or larger. In an embodiment, the filter can have an average pore size that is at least about 1.5 μm or larger. In an embodiment, the filter can have an average pore size that is at least about 5 μm or larger. In an embodiment, the filter can have an average pore size that is at least about 10 μm or larger. As larger pore size filters are utilized, the sample will be easier and quicker to filter as the back pressure decreases with increase in pore size.
Filtering the sample can be accomplished using known methods. In an embodiment, the method of filtering that is chosen can be dictated at least in part on the particular application of the method. For example, the sample can be filtered using a negative vacuum, by applying a positive pressure, by the force of gravity. The particular technique used to filter the sample can depend at least in part on the type of device that is being utilized to carry out the method. For example, in order to utilize a negative vacuum, the device can be configured with a port that can be or reversibly attached to a source of vacuum; and in order to apply a positive pressure, the device can be configured to allow a user to apply a positive pressure by applying a force with their hands. In an embodiment, the sample can be filtered by applying a positive pressure. Filtering using positive pressure (or using the force of gravity) can offer the advantage of easily being able to carry out the method in the field without the need for any further equipment, such as a vacuum pump.
A variety of methods can be used to identify and/or quantify microorganisms, including, but not limited to, microbiological assays, biochemical assays (e.g. immunoassay), nucleic acid analysis, or a combination thereof Specific examples of testing methods that can be used include, but are not limited to, lateral flow assays, titration, thermal analysis, microscopy (e.g., light microscopy, fluorescent microscopy, immunofluorescent microscopy, scanning electron microscopy (SEM), transmission electron microscopy (TEM)), spectroscopy (e.g., mass spectroscopy, nuclear magnetic resonance (NMR) spectroscopy, Raman spectroscopy, infrared (IR) spectroscopy, x-ray spectroscopy, attenuated total reflectance spectroscopy, Fourier transform spectroscopy, gamma-ray spectroscopy, etc.), spectrophotometry (e.g., absorbance, fluorescence, luminescence, etc.), chromatography (e.g., gas chromatography, liquid chromatography, ion-exchange chromatography, affinity chromatography, etc.), electrochemical analysis, genetic techniques (e.g., polymerase chain reaction (PCR), transcription mediated amplification (TMA), hybridization protection assay (HPA), DNA or RNA molecular recognition assays, etc.), adenosine triphosphate (ATP) detection assays, immunological assays (e.g., enzyme-linked immunosorbent assay (ELISA)), cytotoxicity assays, viral plaque assays, techniques for evaluating cytopathic effect, culture techniques such as those that can be done using a growth medium (e.g., agar) and/or 3M PETRIFILM Plates (e.g., and imaged, quantified and/or interpreted using a 3M PETRIFILM Plate Reader (3M Company, St. Paul, Minn.)), other suitable analyte testing methods, or a combination thereof. In an embodiment, the microorganisms can be detected by culturing the microorganisms and counting the colonies. In an embodiment, the microorganisms can be detected colorimetrically, electrochemically, fluorimetrically, or lumimetrically. In an embodiment, the microorganisms can be detecting by culturing, or by utilizing immunoassay, enzyme assays or genetic analysis
In one embodiment, microbiological analyses can be conducted immediately after the sample has been collected and concentrated. After the sample has been filtered, the filter, which contains the microorganisms can be removed for microbiological analysis. In an embodiment, the filter can be placed into a device with semisolid microbiological culture medium. Nonlimiting examples of such devices include Petri dishes containing various agar media, Petri dishes containing EASYGEL® media (Micrology Laboratories, Goshen Ind.), and several types of dry, rehydratable culture media, such as 3M PETRIFILM Aerobic Count Plates (3M Company, St. Paul, Minn.), 3M PETRIFILM Coliform Count Plates, 3M PETRIFILM Coliform/E. coli Count Plates, COMPACTDRY Total Count Plates (Nissui Pharmaceutical Company, Ltd., Tokyo, JP), SANITA-KUN® Coliforms Plate (Chisso Corporation, Tokyo, JP), and the SANITA-KUN Total Aerobic Count Plate. In an embodiment, the dry, rehydratable culture media are rehydrated prior to inserting the filter. An advantage of the disclosed method is that the portable, easy to use method can be used with easy to use rehydratable culture media to perform microbiological analyses in a field location with minimal laboratory equipment, such as a small area or glove box for aseptic transfer of the filter onto the culture media. Optionally, a small incubator could provide temperature control for the incubation of the culture media in a field location.
In an embodiment, the culture medium can be incubated at an appropriate temperature for an appropriate time subsequent to the placement of the filter onto the culture medium. The appropriate temperature and time for the growth of colonies of microorganisms would be known to a person skilled in the art, and could be in accordance with standard methods. Methods as disclosed herein can be used to concentrate microorganisms that are typically found in water samples for example. Microorganisms that are of particular interest in water samples include, for example, coliforms, fecal coliforms, Escherichia coli, and certain species of the genera Pseudomonas, Aeromonas, Enterococcus, Legionella, and Mycobacterium , among others.
Tests for coliforms, for example, can be carried out with incubation at a temperature of approximately 35° C. for 24 to 48 hours; tests for fecal coliforms can be incubated at a temperature of approximately 45° C. After the period of incubation, the filter can be examined for the presence of bacterial colonies and the number and type of each colony can be recorded. Certain microbiological media, such as Violet Red Bile (VRB) agar contain indicators that distinguish certain bacteria, such as, lactose-fermenting bacteria, from others.
In an embodiment, the colonies can be counted manually. When available, devices such as a magnifying lens and/or a dark field magnifying device, such as a Quebec Colony Counter, can be used to assist in counting the colonies. Alternatively the plates can be counted using an automated plate counter such as, for example, ProtoCOL SR or HR colony counting systems from Synbiosis (Fredrick, Md.) or a PETRIFILM Plate Reader from 3M Company, provided the filter and the growth medium used in the procedure are compatible with the automated colony counting system.
In an embodiment, the filter can be removed from the receptacle, placed on a culture dish (specific for growth of particular bacteria or non-specific for total growth), allowed to grow for a certain period of time and the colonies can be detected by use of bioluminescence reagents and imaging of the plate using an imaging system such as MILLIFLEX® Rapid Microbiology Detection and Enumeration System (Millipore, Bedford, Mass.).
In an embodiment, the sample can be collected and concentrated on the filter and the microorganisms can be directly detected thereon by adding bioluminescent reagents to the filter. Bioluminescence can be quantified by either imaging of the filter or measuring bioluminescence in a luminometer.
In an embodiment, the sample can be collected and concentrated on the filter. The filter can optionally be washed, lysis reagents can be added to the filter in order to lyse microorganisms and release the detection analyte such as ATP. The ATP released can be collected and detected by adding bioluminescent reagents to the lysate. Bioluminescence can be quantified by measuring bioluminescence in a luminometer.
In other embodiments, the sample can be collected and concentrated and the entire device can be transferred to a laboratory for detection. In yet another embodiment, the sample can be collected and concentrated, the filter can be removed and placed into a sterile container for transport to a laboratory for detection. In an embodiment, the container can be designed to keep the filter moist during transport, to avoid loss of viability of the microorganisms. Optionally, a preservative can be added to the container to maintain the viability of the microorganisms during transport.
Agitation may include any of the above-described processes, and for example, can be linear, in a circular orbit, an elliptical orbit, a random orbit, a combination thereof, or of other means to ensure effective and efficient mixing of the sample and the concentration agent. The receptacle may be further secured by clamping or other means during agitation to minimize spillage and/or loss of the contents of the receptacle.
In an embodiment, the liquid composition within the receptacle can be agitated by shaking manually by hand. In such an embodiment, the receptacle containing the liquid composition can be manually shaken for about 15 seconds to about 5 minutes. In such an embodiment, the receptacle containing the liquid composition can be manually shaken for about 30 seconds to about 3 minutes. In such an embodiment, the receptacle containing the liquid composition can be manually shaken for about 1 minute to about 2 minutes.
In an embodiment, the liquid composition within the receptacle can be agitated by using a Titer Plate Shaker platform (Lab-Line Instruments, Melrose Park, Ill.). Such an exemplary shaker platform can be operated at settings from 0 to about 10. In an embodiment, the shaker platform can be operated at a setting of 2 which is at about 70 rpm. A receptacle containing a liquid composition can be shaken on such an exemplary shaker platform for about 15 minutes to about 2 hours. In an embodiment, a receptacle containing a liquid composition can be shaken on such an exemplary shaker platform for about 30 minutes to about 90 minutes. In an embodiment, a receptacle containing a liquid composition can be shaken on such an exemplary shaker platform for about 60 minutes (1 hour).
In some embodiments, the liquid composition within the receptacle can be agitated by coupling the sample preparation and delivery system 801 to a Burell Model 75 Wrist Action Shaker (Burrell Scientific, Pittsburgh, Pa.), and agitating at a frequency of 10 to 2000 cycles/minute, and in some embodiments, at a frequency of 200 to 500 cycles/minute for a selected duration of time. In some embodiments, the receptacle can be mounted at a distance from the shaker arm from between 5 cm and 50 cm, and in some embodiments, between 10 cm and 20 cm. In some embodiments, the receptacle can inscribe an arc of 5 degrees to 30 degrees, and in some embodiments, between 15 degrees and 20 degrees. The liquid composition in the receptacle may be agitated for at least 10 seconds, in some embodiments, at least 15 seconds, in some embodiments, at least 30 seconds, in some embodiments, at least 40 seconds, and in some embodiments, at least 60 seconds. In some embodiments, the liquid composition within the receptacle can be agitated for at most 15 minutes, in some embodiments, at most 10 minutes, in some embodiments, at most 5 minutes, and in some embodiments, at most 3 minutes.
In some embodiments, the liquid composition within the receptacle can be vortexed in a VX-2500 Multi-Tube Vortexer (VWR Scientific Products, West Chester, Pa.) at an agitation frequency of 200 to 5000 rpm, and in some embodiments, of 1000 to 3000 rpm for a selected duration of time. The vortex orbit can be linear, circular, elliptical, random, or a combination thereof. In some embodiments, the orbit is between 0.25 cm and 5 cm, and in some embodiments, between 1 cm and 3 cm.
A plurality of receptacles can be agitated simultaneously, by being placed on a plate, an arm or other device, and secured by gravity, clamping or other means for subsequent agitation. For example, in some embodiments, one to about fifty receptacles are agitated simultaneously, and in some embodiments, about 10 to about 25 receptacles are agitated simultaneously on a single agitation device or with multiple agitation devices.
In an embodiment, agitation of the liquid composition within the receptacle may be accomplished with steel ball bearings, magnetic stirring bars, blades, and other means to assist in breaking up and/or dispersing the concentration agent within the sample. The agitation methods described above are included by way of example only and are not intended to be limiting. One of ordinary skill in the art will understand that other similar agitation methods can be employed.
In an embodiment, both step 360 (agitating the sample) and step 370 (incubating the sample) can be carried out on a sample. In an embodiment, the step of agitating and the step of incubating can be carried out at the same time. For example, the concentration agent and sample can be shaken for the entire time that the concentration agent and sample are incubated; the concentration agent and sample can be shaken for at least part of the time that the concentration agent and sample are incubated; or the concentration agent and sample can be shaken and then the concentration agent and sample can be incubated.
The exemplary method depicted in
Further methods for isolating microorganisms from a sample containing sample matrix and microorganisms are also disclosed herein that include the steps of placing a liner, which functions as the receptacle, having an opening in a container to form a receptacle assembly, the container configured to at least partially receive the liner; adding the sample to the liner to form a microorganism-bound composition in the liner, the microorganism-bound composition including concentration agent-bound microorganisms and sample matrix; placing a filter over at least a portion of the opening of the liner; placing a filter support on the filter to form a filter assembly, the filter assembly including the liner, the container, the filter and the filter support; inverting the filter assembly; and filtering the microorganism-bound composition through the filter to collect the concentration agent-bound microorganisms on the filter, during which time the liner is deformed or collapses.
Kits are also disclosed herein. An exemplary kit 600 is illustrated in
General characteristics of receptacles that can be utilized as the receptacle 610 were discussed above. Specific configurations and types of receptacles will also be discussed further below. A kit as disclosed herein can include one or more than one receptacle.
General characteristics of filters that can be utilized as the filter 620 were also discussed above. In an embodiment, a filter has a first surface and a second surface and can generally be planar. As stated above, exemplary filters can include, but are not limited to, a woven or non-woven mesh (e.g., a wire mesh, a cloth mesh, a plastic mesh, etc.), a woven or non-woven polymeric web (e.g., comprising polymeric fibers laid down in a uniform or nonuniform process, which can be calendered), a sieve, glass wool, a frit, filter paper, foam, etc., and combinations thereof. In an embodiment, a filter having an average pore size that is greater than the average pore size of the microorganisms is utilized. In an embodiment, the filter has an average pore size that is smaller than the average size of the concentration agent included in the kit. In an embodiment, filters having average pore sizes that are at least about 1 μm can be utilized. In an embodiment, filters having an average pore size of about 10 μm can be utilized. The ability to utilize such large filter sizes can offer the advantage of being able to filter samples relatively quickly without additional equipment.
General characteristics of concentration agents that can be utilized as the concentration agent 630 were also discussed above. Exemplary concentration agents include, but are not limited to particulate or dispersed gamma-FeO(OH), diatomaceous earth that can be (but need not be) surface-treated with titanium dioxide or fine-nanoscale gold or platinum, metal silicates, or combinations thereof. Generally, processing of a water sample having a volume of about 100 mL can be accomplished with about 10 mg to about 100 mg of concentration agent.
Kits can include one or a plurality of filters, one or a plurality of receptacles, an amount of concentration agent sufficient to process one or a plurality of samples. Kits can also include other optional components. In an embodiment, a kit can include components that can be utilized to detect microorganisms. If desired, one or more additives (for example, lysis reagents, bioluminescence assay reagents, nucleic acid capture reagents (for example, magnetic beads), microbial growth media, buffers (for example, to moisten a solid sample), microbial staining reagents, washing buffers (for example, to wash away unbound material), elution agents (for example, serum albumin), surfactants (for example, Triton™ X-100 nonionic surfactant available from Union Carbide Chemicals and Plastics, Houston, Tex.), mechanical abrasion/elution agents (for example, glass beads), and the like) can be included in a kit as disclosed herein.
An exemplary kit includes concentration agent; and a system for isolating microorganisms from a sample, the system includes a receptacle configured to allow filtering of the sample and to reversibly contain the sample and a concentration agent; and a filter having pores with an average pore size that is larger than the average size of the microorganisms.
One type of exemplary device that can be utilized for carrying out a method as disclosed herein is a vacuum device. An exemplary vacuum device is depicted in
During usage, the filter 720 can be placed on the filter support structure 718 and centered on the ledge 714. The sample compartment 730 is then disposed adjacent to the filter 720 and the sample can be added thereto. The sample can be agitated, incubated, or both with the concentration agent in the sample compartment and then a vacuum can be applied to the filtrate compartment 710 via the vacuum port 712 to cause the concentration agent-bound microorganisms to be filtered from the sample matrix. This will cause the concentration agent-bound microorganism to be collected on the filter 720 and the sample matrix to be collected in the filtrate compartment 710. The sample compartment 730 can be covered, or sealed using a sample cover 740 to minimize or stop spillage of the sample when agitated or transported for example.
An exemplary device that is similar to the device depicted in
Another type of exemplary device that can be utilized to carry out a method as disclosed herein is a positive pressure device. One exemplary positive pressure device that can be utilized includes the device described in the commonly assigned PCT Publication No. WO2008/150779, entitled “DEVICES AND PROCESSES FOR COLLECTING AND CONCENTRATING SAMPLES FOR MICROBIOLOGICAL ANALYSIS”, cited herein.
An exemplary embodiment of this device is depicted in
Prior to using the device 810 to concentrate a liquid sample, a filter 850 is placed on or in an embodiment, inside the removable support 830 (as shown in
In the illustrated embodiment, the removable support 830 includes crossbars 838 which project longitudinally downward from the upper end of the removable support 830 to a floor 837 and extend radially inward from the shelf 836. In this embodiment, the floor 837 has a central opening, the filtrate drain 831, which helps to direct the liquid flow out of the removable support 830, as shown in
The crossbars 838 provide a porous support structure for the filter 850 during the use of the device 810. Although shown as crossbars 838 in
Another exemplary positive pressure type of device can be seen in
A system having similar features to that of the sample preparation system 900 is described in commonly assigned U.S. Patent Application No. 60/989,180, entitled “SYSTEM AND METHOD FOR PREPARING AND ANALYZING SAMPLES”; PCT Publication No. WO 2009/067503, entitled “SAMPLE PREPARATION FOR ENVIRONMENTAL SAMPLING”; PCT Publication No. WO 2007/137257, entitled “SYSTEM AND METHOD FOR PREPARING SAMPLES” ; and U.S. Patent Application No. 60/989,175, entitled “SYSTEM AND METHOD FOR PREPARING AND DELIVERING SAMPLES”; each cited herein.
In some embodiments, as shown in
The container 902 can be formed of a variety of materials including, but not limited to, polymeric materials, metals (e.g., aluminum, stainless steel, etc.), ceramics, glasses, and combinations thereof. Examples of polymeric materials can include, but are not limited to, polyolefins (e.g., polyethylene, polypropylene, combinations thereof, etc.), polycarbonate, acrylics, polystyrene, high density polyethylene (HDPE), polypropylene, other suitable polymeric materials capable of forming a freestanding and/or self-supporting container, or a combination thereof. The container 902 can be translucent (or even transparent), or opaque, and can be any suitable size, depending on the type, amount and size of source to be analyzed. For example, in some embodiments, the container 902 can have a capacity of 50 mL, 100 mL, 250 mL, or larger.
In some embodiments, as shown in
As shown in
The liner 904 can be formed of a variety of materials, including a variety of polymeric materials, including, but not limited to, a polyolefin, including, but not limited to polypropylene (e.g., low density polyethylene (LDPE)), polyethylene, and poly(methylpentene), polyamide (e.g., NYLON®), or a combination thereof. In some embodiments, the liner 904 is formed from a molding process, such as a thermoforming process. The liner 904 can be translucent (or even transparent), or opaque.
In some embodiments, as illustrated in
In some embodiments, the liner 904 is self-supporting and/or freestanding while also being deformable. The term “deformable” is used to refer to a structure that can be altered from its original shape or state by pressure (e.g., positive or negative) or stress. In embodiments employing a deformable liner 904, pressure can be applied to the liner 904 to reduce its size from its original (i.e., unstressed) dimensions. Such pressure can be used to promote removal of the liquid composition 914 (or a filtrate thereof) from the liner 904. In such embodiments, the liner 904 can serve as a deformable self-supporting receptacle that can contain the liquid composition 914. In some embodiments, the deformable self-supporting receptacle is also freestanding.
A system that utilizes a collapsible liner, such as that depicted in
In some embodiments, as shown in
In some embodiments, the liner 904 includes a relatively rigid base 926 and a relatively thin and deformable sidewall 928, such that when pressure is applied to the base 926 in a direction parallel to the longitudinal axis of the liner 904 (e.g., via the aperture 924 in the container 902), the liner 904 deforms in the longitudinal direction (e.g., by virtue of the sidewall 928 collapsing rather than the base 926). Alternatively, or in addition, the base 926 can be thicker than the sidewall 928. By way of example only, in some embodiments, the thickness of the sidewall 928 is at least 50 μm, in some embodiments, at least 100 μm, in some embodiments, at least 150 μm, and in some embodiments, at least 200 μm. In some embodiments, the thickness of the base 926 is at least 225 μm, in some embodiments, 275 μm, in some embodiments, at least 300 μm, and in some embodiments, at least 350 μm.
The liner 904 can further include one or more of baffles, pleats, corrugations, seams, joints, gussets, weakened portions (e.g., annular weakened portions), or a combination thereof, which may be incorporated to assist in controlling the deformability of the liner 904, and/or can further reduce the internal volume of liner 904. In some embodiments, the liner 904 can include an accordion-type configuration. In some embodiments, liner 904 does not include any grooves on its internal surface, particularly, at the internal junction between the base 926 and the sidewall 928.
In some embodiments, the liner 904 is deliberately deformed to impart a disruption to the surface geometry of the liner 904. Such a disrupted surface geometry can assist in the breakup of the source during agitation. For example, in some embodiments, an obstruction (e.g., a relatively rigid material) can be positioned between the sidewall 928 of the liner 904 and the container 902 to create a different surface geometry in the sidewall 928 of the liner 904.
As shown in
The system 900 also includes a lid 906. As shown in
As seen in
The filter support 982 can be formed of the same material as the lid 906 or a different material. The filter support 982 may be flexible, or semi-rigid. In some embodiments, the filter support 982 is formed from a nylon nonwoven or woven fabric, while the lid 906 is an injection molded part formed of a polymer, such as polypropylene. In such embodiments, the nylon filter support 982 can be coupled to the lid 906 via an ultrasonic welding technique. During ultrasonic welding, at least a portion of the lower inner circumferential edge 968 can melt to mechanically bond the filter support 982. Since nylon has a higher melting temperature than polypropylene, the nylon filter support 982 can maintain its structural integrity during the ultrasonic welding process. In such embodiments, at least a portion of the lower inner circumferential edge 968 can enter into a portion of filter support 982, thereby encapsulating a portion of the filter support 982.
The filter support 982 can have dimensions and shapes that vary for a given application. The filter support 982 can have any desired shape including, but not limited to, a circular shape, a square shape, a rectangular shape, a triangular shape, a polygonal shape, a star shape, other suitable shapes, and combinations thereof. In the embodiment illustrated in
The dimensions of the filter support 982 may vary depending on the size of the lid 906. In some embodiments, the filter support 982 has a largest dimension (i.e., length, width, or diameter) ranging from 15 mm to 100 mm, although the filter support 982 may have smaller or larger dimensions. For example, in some embodiments, the filter support 982 can have a circular shape and a diameter of 56 mm.
In some embodiments the filter 934 can have a total surface area that is greater than a smallest cross-sectional area of the lid 906. In the lid 906, the smallest cross-sectional area is the cross-sectional area of lid opening 954.
In the embodiment illustrated in
A variety of coupling means can be employed either between the lid 906 and the liner 904, the lid 906 and the container 902, and/or the collar 908 and the container 902 to allow the respective components to be removably coupled to one another, including, but not limited to, gravity (e.g., one component can be set atop another component, or a mating portion thereof), screw threads, press-fit engagement (also sometimes referred to as “friction-fit engagement” or “interference-fit engagement”), snap-fit engagement, magnets, adhesives, heat sealing, other suitable removable coupling means, and combinations thereof. In some embodiments, the sample preparation system 900 need not be reopened after the liquid composition 914 is added, such that the container 902, the liner 904, the lid 906 and the collar 908 need not be removably coupled to one another, but rather can be permanently or semi-permanently coupled to one another. Such permanent or semi-permanent coupling means can include, but are not limited to, adhesives, stitches, staples, screws, nails, rivets, brads, crimps, welding (e.g., sonic (e.g., ultrasonic) welding), any thermal bonding technique (e.g., heat and/or pressure applied to one or both of the components to be coupled), snap-fit engagement, press-fit engagement, heat sealing, other suitable permanent or semi-permanent coupling means, and combinations thereof. One of ordinary skill in the art will recognize that some of the permanent or semi-permanent coupling means can also be adapted to be removable, and vice versa, and are categorized in this way by way of example only.
The liner 904 can also include a lip 944 that projects radially outwardly from the sidewall 928 of the liner 904, and which can form an abutting relationship with an upper surface 946 of the container 902 and the lip 940 of the lid 906, such that when the sample preparation system 900 is assembled, the lip 944 of the liner 904 is positioned between the lip 940 of the lid 906 and the upper surface 946 of the container 902, and a seal (e.g., a hermetic seal) is formed. As shown in
A system as disclosed in
The above-described means for assembling the sample preparation system 900 and for forming a seal between the components of the sample preparation system 900 are described and illustrated by way of example only. One of ordinary skill in the art will understand, however, that a variety of other mechanisms could be employed to assemble the components of the sample preparation system 900 and to form a seal (e.g., a liquid-tight seal, a hermetic seal, or a combination thereof), such that the sample preparation system 900 is inhibited from leaking under normal operating conditions.
While the lid 906 of the embodiment illustrated in
The lid 906 can be formed of a variety of materials, including the materials listed above with respect to the container 902. The lid 906 can be translucent (or even transparent), or opaque, depending on the application of use.
The collar 908 can be formed of a variety of materials, including, but not limited to a variety of polymeric materials, metal materials, and combinations thereof. For example, the collar 908 can be formed of a molded plastic component, or a machined metal (such as aluminum) component. In some embodiments, the collar 908 is formed of a molded plastic component comprising glass fiber reinforced polypropylene.
As shown in
In the embodiment shown in
One such device can be made by modifying a 3M PPS™ Paint Preparation System, commercially available from 3M Company (St. Paul, MN). Example 2 that follows illustrates an exemplary method for modifying the 3M PPS Paint Preparation System to obtain a system that can be utilized herein.
Devices that utilize the force of gravity to filter the concentration agent-bound microorganisms from the sample matrix can also be utilized herein. In an embodiment, the devices described above can function as gravity filtration devices in that a vacuum is not applied, or the sample matrix (filtrate) is not forced through the filter via pressure on the receptacle. Other types of systems (besides vacuum filtration, positive pressure systems and gravity filtration systems) can also be utilized herein.
Also described herein are systems for isolating microorganisms from a sample, the sample including sample matrix and microorganisms, the system including: a liner configured to afford contact of a concentration agent and the sample, to provide a microorganism-bound composition that comprises concentration agent having bound microorganisms and sample matrix; a filter, the filter having a first surface and a second surface and having pores having an average pore size that is larger than the average size of the microorganisms; a filter support configured to contact the first surface of the filter and afford contact of the microorganism-bound composition with the second surface of the filter, wherein the liner and filter support are configured to afford filtration of the microorganism-bound composition through the filter in order to collect the concentration agent-bound microorganisms on the second surface of the filter.
All cultures were obtained from The American Type Culture Collection (ATCC, Manassas, Va.).
A microporous polyvinylidene fluoride (PVDF) film was prepared using a 40 mm twin screw extruder. PVDF polymer pellets (3M/Dyneon 1012) were introduced into the hopper of the extruder. The extruder was set with a screw speed of 150 RPM. The nucleating agent (HYPERFORM® HPN-68L), in powder form, was premixed in a 2 liter batch with the glycerol triacetate diluent (TRIACETIN® glycerol triacetate) with a ULTRA TURRAX® T-25 Basic high shear mixer from IKA Works, Inc. (Wilmington, N.C.) for a period of about 5 minutes (there is only one speed for the unit) to uniformly distribute the powder in a non-agglomerated, non-gritty, smooth to the touch state and then fed, with additional diluent, by a feeding device into the extruder via a port. The PVDF polymer/diluent/nucleating agent weight ratio was 39.85/60.00/0.15 respectively. The total extrusion rate was about 13.6 kg/hr; the cast speed was 1.6 m/min. The extruder had eight zones with a temperature profile of zones 1 to 8 at 188° C. The uniformly mixed polymer/diluent/ nucleator melt was subsequently pumped through a double-chromed coat-hanger slot film die maintained at 166° C., and cast onto a patterned casting wheel maintained at a wheel temperature of 71° C. at a speed of 3.0 meters per minute (m/min) to form a film. The film was washed in-line at a wash station with deionized water and was air dried. The washed film was continuously fed into a length orienter and stretched with an inline film stretch ratio of 1.6×2.2 at 132° C. The roll of membrane was evaluated and found to have the following properties: an average film thickness of 1.17 mm; a bubble point pore size of 11.8 μm; a Gurley resistance to air flow of 0.4 sec/50 cc; and a resistance to water flow of 1.4 sec/100 cc. Further details regarding manufacture of this filter can be found in the PCT Publication No. WO 2009/048743, entitled “MICROPOROUS MEMBRANES HAVING A RELATIVELY LARGE AVERAGE PORE SIZE AND METHODS OF MAKING THE SAME”, cited herein.
The PVDF filter was then further processed to prepare a hydrophilic polyalkylene glycol di(meth)acrylate functionalized large pore size PVDF membrane by saturating the membrane with a 10 weight percent solution of SR344 (Sartomer Co., Inc., Exton, Pa.) in methanol. The sample was then irradiated with an electron beam at a dose of 20 kilograys (kGy), rinsed three times with water and placed in water that was heated to 70° C. for one hour. Further details regarding processing of this filter can be found in Example 9 of U.S. Pat. No. 7,553,417, entitled, “FUNCTIONALIZED SUBSTRATES”, cited herein.
An isolated E. coli (ATCC 51813) colony was inoculated into 5 ml BBL Trypticase Soy Broth (Becton Dickinson, Sparks, Md.) and incubated at 37° C. for 18-20 hours. This overnight culture at approximately 109 colony forming units/ml (CFU/ml) was diluted in Butterfield's Buffer (pH 7.2, VWR, West Chester, Pa.). A 1:1000 further dilution from a 102 cfu/ml dilution was done in 100 ml of potable water resulting in a final concentration of 0.1 /ml (10 cfus total).
A device as described in PCT Application No. US2008/064939, entitled “DEVICES AND PROCESSES FOR COLLECTING AND CONCENTRATING SAMPLES FOR MICROBIOLOGICAL ANALYSIS”, cited herein, was wiped down with 70% isopropyl alcohol in water solution, allowed to air dry for 30 minutes and then washed with sterile deionized water. After additional air drying for 30 minutes, a 4.4 cm diameter membrane filter of pore size 10 microns was placed onto the removable support of the device. The support was tightened to the body of the device using the lock ring, and the exit port was sealed using a 3.3 cm diameter piece of SCOTCH® packaging tape (3M Company, St. Paul, Minn.), followed by addition of the spiked sample. 100 milligrams of amorphous, spheroidized magnesium silicate concentration agent (sold as 3M Cosmetic Microspheres, [CM-111], 3M Company, St. Paul, Minn.) were added. The plunger was placed on top the device to cover it and then the contents in the device were mixed by shaking manually at room temperature (25° C.) for 2 minutes.
After mixing, the adhesive barrier seal was removed and pressure was applied by manually pushing down the plunger in the device for approximately5 minutes to capture the amorphous, spheroidized magnesium silicate concentration agent on the filter. During this step the sample was drained out of the device thru an exit port at the bottom of the device. After filtration the device was opened to expose the filter. The filter was removed from the lid using sterile forceps and placed concentration agent side up on 3MPETRIFILM E coli/Coliform Count Plate. The plate was hydrated with 1 ml sterile Butterfield's Buffer, sealed and incubated in a 37° C. incubator per manufacturers instructions. A 1:1000 dilution from the initial 102 cfu/ml was plated as control on 3MPETRIFILM E coli/Coliform Count Plate. Following overnight incubation the plate was analyzed for bacterial colonies per manufacturers instructions.
Results (Capture Efficiency) were calculated using the following formula:
Out of a total 8 cfus of E. coli spiked in 100 ml, 8 cfus were obtained on the plated amorphous, spheroidized magnesium silicate covered filter, resulting in a capture efficiency of 100%.
A 3M PPS Paint Preparation System was obtained and modified as follows. The lid with mesh support was generated using a Dremel cutting wheel to remove the lower support ring from the 3M PPS Paint Preparation System lid. The resulting surface was sanded smooth using 100 grit Wet-or-Dry sandpaper (3M Company, St. Paul, Minn.). The adapter ring was generated in a similar fashion from a second lid using a Dremel cutting tool to remove the top portion of a 3M PPS Paint Preparation System lid followed by sanding. These modifications allowed the filter to be “pinched” around its perimeter between the smooth surfaces of the lid and adapter ring during device assembly. The final modification was to cut a larger hole in the base of the outer cup to facilitate access to the liner during sample processing. Assembly and use of the device is described below.
A microporous polyvinylidene fluoride (PVDF) film was prepared using a 40 mm twin screw extruder. PVDF polymer pellets (3M/Dyneon 1012) were introduced into the hopper of the extruder. The extruder was set with a screw speed of 150 RPM. The nucleating agent (HYPERFORM® HPN-68L), in powder form, was premixed in a 2 liter batch with the glycerol triacetate diluent (TRIACETIN® glycerol triacetate) with a ULTRA TURRAX® T-25 Basic high shear mixer from IKA Works, Inc. (Wilmington, N.C.) for a period of about 5 minutes (there is only one speed for the unit) to uniformly distribute the powder in a non-agglomerated, non-gritty, smooth to the touch state and then fed, with additional diluent, by a feeding device into the extruder via a port. The PVDF polymer/diluent/nucleating agent weight ratio was 39.85/60.00/0.15 respectively. The total extrusion rate was about 13.6 kg/hr; the cast speed was 1.6 m/min. The extruder had eight zones with a temperature profile of zones 1 to 8 at 188° C. The uniformly mixed polymer/diluent/ nucleator melt was subsequently pumped through a double-chromed coat-hanger slot film die maintained at 166° C., and cast onto a patterned casting wheel maintained at a wheel temperature of 71° C. at a speed of 3.0 meters per minute (m/min) to form a film. The film was washed in-line at a wash station with deionized water and was air dried. The washed film was continuously fed into a length orienter and stretched with an inline film stretch ratio of 1.6×2.2 at 132° C. The roll of membrane was evaluated and found to have the following properties: an average film thickness of 1.17 mm; a bubble point pore size of 11.8 μm; a Gurley resistance to air flow of 0.4 sec/50 cc; and a resistance to water flow of 1.4 sec/100 cc. Further details regarding manufacture of this filter can be found in the PCT Publication No. WO 2009/048743, entitled “MICROPOROUS MEMBRANES HAVING A RELATIVELY LARGE AVERAGE PORE SIZE AND METHODS OF MAKING THE SAME”, cited herein.
The PVDF filter was then further processed to prepare a hydrophilic polyalkylene glycol di(meth)acrylate functionalized large pore size PVDF membrane by saturating the membrane with a 10 weight percent solution of SR344 (Sartomer Co., Inc., Exton, Pa.) in methanol. The sample was then irradiated with an electron beam at a dose of 20 kilograys (kGy), rinsed three times with water and placed in water that was heated to 70° C. for one hour. Further details regarding processing of this filter can be found in Example 9 of U.S. Pat. No. 7,553,417, entitled, “FUNCTIONALIZED SUBSTRATES”, cited herein.
An isolated E. coli (ATCC 51813) colony was inoculated into 5 ml BBL Trypticase Soy Broth (Becton Dickinson, Sparks, Md.) and incubated at 37° C. for 18-20 hours. This overnight culture at approximately 109 colony forming units/ml (CFU/ml) was diluted in Butterfield's Buffer (pH 7.2, VWR, West Chester, Pa.). A 1:1000 further dilution from a 102 cfu/ml dilution was done in 100 ml of potable water resulting in a final concentration of 0.1 /ml (10 cfus total). The liner was placed in the cup, followed by addition of the spiked sample. 100 milligrams of amorphous, spheroidized magnesium silicate concentration agent (sold as 3M Cosmetic Microspheres, [CM-111]) were added. The adapter ring was then placed on the liner followed by placing the PVDF membrane (pore size 10 microns) cut to the outer diameter of the lid (6.6 cm) on the adapter ring. The lid containing the nylon support mesh was placed on the filter and tightened using the lock ring.
The contents were mixed at room temperature (25° C.) for 60 minutes on a Titer Plate Shaker platform (Lab-Line Instruments, Melrose Park, Ill.) at approximately 70 rpm setting. After the incubation the devices were turned upside down, and pressure was applied by manually compressing the inner liner for approximately 1.5 minutes to capture the concentration agent on the filter. During this step the filter was supported by the nylon mesh. After filtration the lid was removed to expose the filter. The filter was removed from the lid using sterile forceps and placed concentration agent side up on Tryptic Soy Agar (TSA) plates and cultured overnight in a 37° C. incubator. The plates were analyzed manually for bacterial colonies. A 1:1000 dilution from the initial approximately 102 cfu/ml was plated as control on 3MPETRIFILM E coli/Coliform Count Plate. The plate was incubated in a 37° C. incubator overnight the plate was analyzed for bacterial colonies per manufacturers instructions. Colonies on the TSA plates with the plated concentration agent covered filter were counted manually.
The capture efficiency was calculated as shown in Example 1 above. Out of a total 17 cfus (average of n=2, standard deviation 8%) spiked in 100 ml, an average count of 17 cfus was obtained on the plated concentration agent covered filter. An average (n=2) capture efficiency of approximately 100% (standard deviation 11%) was observed.
3M PPS Paint Preparation Systems were modified as explained in Example 2 above. An isolated E. coli (ATCC 51813) colony was inoculated into 5 ml BBL Trypticase Soy Broth (Becton Dickinson, Sparks, Md.) and incubated at 37° C. for 18-20 hours. This overnight culture at approximately 109 colony forming units/ml (CFU/ml) was diluted in Butterfield's Buffer (pH 7.2, VWR, West Chester, Pa.). A 1:1000 further dilution from a 102 cfu/ml dilution was done in 100 ml of potable water resulting in a final concentration of 0.1 /ml (10 cfus total). The liner was placed in the cup, followed by addition of the spiked sample. 250 milligrams of various concentration agents were added (see Table 1 for specific concentration agents). The X296-Talc was produced as seen in U.S. Pat. No. 6,045,913; and CM-111 in the table refers to 3M Cosmetic Microspheres, [CM-111]. The adapter ring was then placed on the liner followed by placing either a nylon membrane (F150A0A or F15000A 3M CUNO, pore size 1.1-1.4 μm) or a PVDF membrane (made according to U.S. Pat. No. 7,338,692 having a pore size of 1 μm) cut to the outer diameter of the lid (6.6 cm) onto the adapter ring. The lid containing the nylon support mesh was placed on the filter and tightened using the lock ring.
The contents were mixed at room temperature (25° C.) for 60 minutes on a Titer Plate Shaker platform (Lab-Line Instruments, Melrose Park, Ill.) at approximately 70 rpm setting. After the incubation the devices were turned upside down, and pressure was applied by manually compressing the inner liner for approximately 1.5 minutes to capture the concentration agent on the filter. During this step the filter was supported by the nylon mesh. After filtration, the lid was removed to expose the filter. The filter was removed from the lid using sterile forceps and placed concentration agent side up on Tryptic Soy Agar (TSA) plates and cultured overnight in a 37° C. incubator. The plates were analyzed manually for bacterial colonies.
The capture efficiency was calculated as shown in Example 1 above and is reported in Table 1 below. The capture data was obtained from TSA plates on which the retrieved concentration agent on filters had been plated. Amongst bacterial growth on test plates, only colonies characteristic of E. coli (1-1.5 mm in diameter, beige, dome shaped) were counted.
E. coli
E. coli
Filtration rates using modified 3M PPS Paint Preparation Systems as explained in Example 2 were determined. Membrane flow rates were measured using a vacuum filtration apparatus (Air Cadet, Barnant Company, Barrington, Ill.) set to a vacuum pressure of −10 inches of mercury. The following filters were obtained: Gelman NYLAFLO® 0.2 μm pore size (obtained from VWR, West Chester, Pa.); StratageneDuralon 0.42 μm pore size (Stratagene, La Jolla, Calif.); F150A0A or F15000A 3M CUNO, pore size 1.1-1.4 μm; and a PVDF membrane made according to U.S. Pat. No. 7,338,692 having a pore size of 1 μm. 48 mm disks of the membranes were cut from larger pieces of membrane and placed in the filter housing. The vacuum was turned on and 100 mL of 18 megaohm water (MILLI-Q® Biocel; Millipore; Bedford, Mass.) was added to the receptacle. The amount of time necessary to filter the sample using each type of filter was measured using a stopwatch. The mean time for each membrane was determined from the average of three replicate samples, as shown in Table 2.
Filtration times for water samples (100 mL) containing 250 mg spheroidized magnesium silicate concentration agent (sold as 3M Cosmetic Microspheres, [CM-111]) and X296-Talc (produced as seen in U.S. Pat. No. 6,045,913) were also measured. By increasing the pore size of the membrane, the amount of time required to filter 100 mL samples was decreased. The presence of the particles did not significantly increase the filtration time. Reference membranes typical of those used for filtration of bacteria (pore sizes of 0.2 to 0.5 micrometers) were included in the analysis for comparison. The results can be seen in Table 2 below.
Thus, embodiments of methods, kits and systems for processing samples are disclosed. One skilled in the art will appreciate that the present disclosure can be practiced with embodiments other than those disclosed. The disclosed embodiments are presented for purposes of illustration and not limitation, and the present disclosure is limited only by the claims that follow.
This application claims the benefit of U.S. Provisional Patent Application No. 61/141,813, filed Dec. 31, 2008.
| Number | Date | Country | |
|---|---|---|---|
| 61141813 | Dec 2008 | US |
| Number | Date | Country | |
|---|---|---|---|
| Parent | 13142292 | Sep 2011 | US |
| Child | 14747837 | US |
