Journal of Non-Crystalline Solids 285 (2001) 303±308 www.elsevier.com/locate/jnoncrysol Aerogels as biosensors: viral particle detection by bacteria immobilized on large pore aerogel Mary Power a, Bouvard Hosticka a, Eric Black b, Chuck Daitch b, Pamela Norris a,* a Mechanical and Aerospace Engineering, University of Virginia, 570 Edgemont Road, Charlottesville, VA 22903, USA b Veridian-Paci®c Sierra Research, Charlottesville, VA, USA Abstract A proof-of-principle study is reported in which bacteria were immobilized within macroporous, supercritically dried silica sol±gel discs and signal induction was demonstrated by aerosolized virus particles. Escherischia coli (pET-gfp) bacteria-doped gels were used as an aerosol collector to detect bacteriophage. The bacteriophage (105 and 108 plaque forming units/ml) (pfu/ml) were aerosolized through the discs for 10 min, at a ¯ow rate of 1.75 l/min and aerosol humidity of 70%. The discs were then incubated in bacterial growth media for 4 h and green ¯uorescent protein (GFP) expression monitored. The induction of GFP indicated that both bacteriophage and bacteria survived the stressful desiccating conditions of the aerosol challenge. Scanning confocal laser microscopic (SCLM) analysis demonstrated that the bacteriophage contacted viable bacteria and induced expression of the GFP in 35±95% of the bacterial cells. These ®ndings indicate that virus particles can penetrate the structure of macroporous silica gels and trigger a detectable response in immobilized bacteria. The goal is to use microorganisms immobilized within these materials to facilitate the detection of chemicals and organisms within the environment. Ó 2001 Elsevier Science B.V. All rights reserved. PACS: 82.33.; 87.80 1. Introduction Sol±gel-derived silica holds promise as a biocompatible scaold for the immobilization of cells in a variety of applications. The use of aerogel as a matrix in the design of biosensors is an interesting proposition due to several unique characteristics of aerogels, primarily their highly porous nature, adjustable pore size and extremely large internal surface area. The goal is to use microorganisms * Corresponding author. Tel.: +1-804 924 6295; fax: +1-804 982 2037. E-mail address: [email protected] (P. Norris). immobilized within this material and together, facilitate the collection of aerosols and detection of chemicals and/or organisms within the environment. Silica, regardless of origin, has always been a useful matrix for the immobilization of biological materials. Silica is both chemically and mechanically robust and biocompatible. A diculty of most aerogel production routes for cell immobilization is the resulting small pore size. Uo et al. [1] used pre-gelled macroporous silica matrices that contained water-soluble polymers in order to increase the pore diameter. The polymers were removed by rinsing, yielding macroporous silica. Saccharomyces cereviciae was loaded and upon 0022-3093/01/$ - see front matter Ó 2001 Elsevier Science B.V. All rights reserved. PII: S 0 0 2 2 - 3 0 9 3 ( 0 1 ) 0 0 4 7 1 - 9 304 M. Power et al. / Journal of Non-Crystalline Solids 285 (2001) 303±308 incubation showed germination. Others have shown that optimal cell growth in ceramics has been achieved with pore diameters between one and ®ve times the size of the cells [2,3]. It was determined that the macroporous production route described by Kazi et al. [4] resulted in pore diameters in the desired range and its ability to be colonized by Escherischia coli cells is described. Whole-cell living bioreporters are of interest in biosensor development since they can be used to detect real time physical eects [5]. Light can be measured non-invasively and sensitively without disrupting the cells and this therefore enables in situ and on-line monitoring. Green ¯uorescent protein (GFP) is a naturally occurring protein from the jelly®sh Aequorea victoria. This protein has great potential as a bioreporter since it is easily detected and requires no additional energy, other than that required for protein expression, to emit ¯uorescence. The gene for this protein was cloned behind a promoter that required a polymerase enzyme produced solely by bacteria infected with T7 bacteriophage viruses, in order to express the protein [6]. The bacteriophage, in an aerosol stream, were then monitored. This paper describes the integration of macroporous supercritically dried and re-wetted silica gels as a colonization scaold for bacteria, an aerosol collection device and a biosensor system. mother liquor. Samples were supercritically dried using carbon dioxide to remove the ethanol and to retain monolith structure. The resulting macroporous gels (q 400 kg=m2 ) were machined into discs of 47 mm diameter and 1 mm thickness. The dry discs were soaked for 24 h in phosphate buered saline (PBS; pH 7.2) and then subjected to 20 min mild sonication in a Bransonic 2000 sonic bath in order to replace the air in the pores with liquid. The wetted discs were then placed into ®lter holders. Bacteria (1 lm length) in liquid media were ¯owed through the disc at a ¯ow rate of 0.8 ml/min for 2 h. The discs were then stored in fresh NZY bacterial growth media (Fisher Scienti®c) and 10 mM MgSO4 at 30°C for 4 h, and then at 4°C until use (for up to 4 days). Samples of these discs were also processed for SEM. The bacteria used in this study were E. coli carrying a plasmid (pET-gfp)with the gene for GFP under the control of the bacteriophage T7 polymerase promoter [6]. The presence of bacteriophage T7 polymerase is required for the expression of GFP in this system, creating a tightly controlled system whereby green ¯uorescence is only observed if the virus particles have come into contact with the bacteria. 2. Experimental The aerosol generation system consists of a small air compressor with a HEPA ®lter and dessicator supplying regulated air at 125 kPa to a TSI model 3075 constant output atomizer run in the recalculation mode. Bacteriophage CE6 virus particles (70 nm diameter) were suspended in PBS pH 7.0, 10 mM MgSO4 , and 2% trehalose. The phage concentration in the liquid was 105 or 108 plaque forming units/ml (pfu/ml). The aerosolizer was run at a ¯ow of 1.75 l/min. The E. coli-doped aerogel discs were placed in the test chamber of the aerosol generation system and the ¯ow was directed through 7 mm diameter apertures in fenestrated partitions housing the large pore aerogel±aerosol collector. The aerosol humidity was run at 70%. The dierential pressure across the 1 mm thick discs was of the order of 15 2.1. Production of macroporous silica aerogel aerosol collectors Macroporous silica sol±gels were fabricated by the method of Kazi et al. [4]. Brie¯y, formamide (45.72 g) was combined with 1.4 M nitric acid (12 g) in a 125 ml polypropylene mold. The mixture was stirred in an ice bath until it had reached a temperature less than 5°C. Tetramethyl orthosilicate (61.9 g) was added rapidly, and the mold was sealed and agitated until the solution was homogeneous. The sample was then placed in a 50°C oven for 12 h. Following gelation, the material was removed from the mold and subsequent 1 M nitric acid and ethanol washes were used to remove the 2.2. Aerosol generation, collection and detection of bacteriophage virus particles M. Power et al. / Journal of Non-Crystalline Solids 285 (2001) 303±308 kPa, dropping in 10 min runs to approximately 5 kPa as the gel dried out. The discs were recovered from the aerosol collection device and wetted with 500 ll NZY media. The discs were incubated for 4±8 h at 30°C. The expression of GFP was monitored by ¯uorescence microscopy and by scanning confocal laser microscopy (SCLM). A universal DNA stain, Syto17 (Molecular Probes, Eugene, Oregon), was used to detect the total number of E. coli cells within the material. The results were expressed as the ratio of GFP expressing cells to the total cell population in each microscopic ®eld of view. Three results were averaged for each data point and the S.D. for all the measurements was used for the error bars shown. The error bars represent a measure of the repeatability. 3. Results The wetted macroporous silica sol±gel provided a suitable matrix for microbial colonization. SEM micrographs of the uncolonized gel show macropores ranging in size from approximately 10 to 100 lm (Fig. 1). The majority of the gels survived the wetting and ¯ow procedure although cracking did occur at the edges of the discs. Bacterial pen- 305 Fig. 1. A SEM micrograph of a macroporous silica gel disc produced by supercritical drying examined prior to colonization by bacteria. Macropores of the order of 10±100 lm are apparent. etration of the wetted aerogel discs was observed using SEM analysis. Bacteria were observed over the entire 1 mm depth. Large numbers of cells, often observed in clusters, accumulated on or near the disc surface (Fig. 2(a)). However, smaller clusters and individual cells were also observed deep within the porous network (Fig. 2(b)). Using SCLM the extent of colonization at different depths could be approximated. Fig. 3 is a Fig. 2. SEM micrographs of a cross-section of a macroporous silica gel disc that had been colonized with E. coli (pET-gfp). Panel A is the surface closest to the ¯ow and Panel B is an area near the middle of the disc. Large numbers of bacteria are evident. Arrows indicate clusters of bacterial cells. 306 M. Power et al. / Journal of Non-Crystalline Solids 285 (2001) 303±308 representative scan depicting the number of bacterial cells per ®eld of view at a single x y location at various depths (z-axis). Depth 0 mm is the surface in the direction of bacterial ¯ow when colonizing and as would be expected the largest number of bacteria were observed at this surface. The limit of the SCLM under these conditions was 0.3 mm on either side of the disc. The disc was turned over and examined from the reverse side at the same x y location. Bacteria were observed at all depths with a consistent, slight increase in numbers at the bottom surface. Although the counts at the dierent x y locations on individual discs varied a great deal, the general trend illustrated in Fig. 3 was conserved. The collector integrity was maintained in most of the viral aerosol challenges although occasionally the disc cracked. The cracked discs were discarded. The intact collectors were examined by SEM following the virus aerosol challenge and a further 4 h incubation in liquid media, which was required for optimum GFP production. The presence of elongated cells and dividing cells gave a strong indication that the bacteria were still viable and growing (Fig. 4). This suggested that mass transport of nutrients provided by the bacterial growth media and waste materials is occurring within the gel matrix. The elongated cells may Fig. 3. A representative depth pro®le of bacterial colonization through the thickness of a disc. The bacterial numbers are the total number of Syto 17 stained E. coli at a single x y location (®eld of view) as determined by SCLM. The limit of this microscope and the macroporous gel discs was 0.3 mm into the sample. The sample was turned over and scanned at the same x y coordinates. be bacteria exhibiting a form of stress response, possibly due to the overproduction of GFP. The immobilized E. coli cells were receptive to infection by the aerosolized virus particles. This indicated that both the bacteria and the viruses survived the stressful conditions they were subjected to in the aerosol. The protocol that resulted in optimum expression of GFP by the entrapped bacteria was a 10 min aerosol exposure to 108 pfu/ ml phage, in the aerosolized liquid, at a humidity of 70%. This optimum exposure resulted in a large percentage of the bacteria expressing GFP as determined by ¯uorescent microscopy. Using 97 nm ¯uorescent beads to simulate the phage it was calculated that this would result in the deposition of 8 104 pfu/mm2 of macroporous gel surface for a total of 2 105 pfu (data not shown). The virus concentration in the aerosol was varied in an attempt to determine the microscopic detection limits. Serial 10-fold dilutions of the phage culture were made in PBS containing 2% trehalose, and 10 mM MgSO4 . The maximum dilution of the phage in the ¯uid to be aerosolized resulting in detectable expression across the entire disc, as determined by microscopic visualization, was 105 pfu/ml, in the liquid (Fig. 5). All further Fig. 4. SEM micrograph of E. coli (pET-gfp) in the collector disc after having been subjected to the 10 min aerosol stream of viral particles. The black arrow depicts healthy looking dividing cells and the white arrow depicts elongated cells, growing but probably stressed. M. Power et al. / Journal of Non-Crystalline Solids 285 (2001) 303±308 307 It was determined a 10 min aerosol collection of this dilution would result in 2 103 pfu ¯owing through the aerogel. At this phage concentration (105 pfu/ml), GFP expression appeared to be induced over the entire 1 mm depth of the collector. The ratio of GFP producing cells to the total number of bacteria present (Syto17 stained cells) was determined at a number of sites for three aerosol collector discs. The SCLM data are presented in Fig. 6. At the surface of the gels, a mean of 95% of the detectable bacteria expressed GFP indicating that they had been infected with the bacteriophage virus. The percentage of cells infected dropped across the 1 mm thickness with 35% of the cells expressing GFP at the surface furthest from the aerosol. Fig. 5. A SCLM micrograph of GFP producing E. coli (pETgfp) taken 100 lm from the surface of the disc exposed to the aerosol. This bacteria colonized disc had been exposed to CE6 lambda bacteriophage virus particle (105 pfu/ml) for 10 min. This dilution of phage was found to be the limit of reasonable detection by SCLM. studies were carried out at this maximum dilution. The ¯uorescent bead data described above were used to calculate the expected number of virus particles contacting the macroporous gel surface. Fig. 6. Ratio of the number of GFP expressing E. coli compared to the total number stained with Syto17. The values are mean and S.D. of counts of scans from three macroporous discs colonized with E. coli and subjected to viral aerosolization. The limit of this microscope and the discs was 0.3 mm into the sample. The sample was turned over and scanned at the same x y coordinates. 4. Discussion Cloning of the GFP protein behind the T7 polymerase promoter resulted in a system by which GFP expression could be easily controlled. Maintaining the T7 polymerase in the CE6 phage gave an elegant model whereby the viral particles were required to infect a bacterial cell in order for GFP to be produced. This system was developed in order to test the feasibility of using wetted macroporous silica sol±gel-derived materials as support matrices for living organisms to be used as biosensors. The use of chemiluminescent and bioluminescent reporter systems to detect organic environmental pollutants is an area that is of growing interest [5]. There is also an interest in developing these systems for bio-warfare agent detection. The macroporous gel used had pores of the order of 10±100 lm, which is in the range that is determined optimal for cell colonization and growth [7]. The presence of clusters of cells and obviously dividing and growing cells (Fig. 4) suggest that indeed transport of nutrient and waste products was occurring into the wetted gel. Nutrient transport, including oxygen, is also required for GFP expression con®rming that cells even deep within the aerogel were viable. Although the pore network within aerogels is tortuous bacteria were observed throughout the 1 mm thickness of the 308 M. Power et al. / Journal of Non-Crystalline Solids 285 (2001) 303±308 discs, indicating that there were interconnected routes of at least 1 lm in diameter. The viral particles in the aerosols were also able to penetrate the entire 1mm disc thickness and contact viable E. coli cells as evidenced by green ¯uorescence observed by SCLM (Figs. 5 and 6). As with the bacterial colonization, more viruses were collected near the surface of the discs. The percentage of bacterial cells infected with phage decreased rapidly across the aerogel ®lter with 95% infected at the surface and only 35% infected at the opposite side (Fig. 6). This is presumably partially because the concentration of viruses decreased in the aerosol as they were ®ltered out across the disc. Also, there were fewer bacteria present further into the disc, decreasing the likelihood of contact between the two being made. Variable distribution of bacterial cells within the aerogel matrix and such things as clumping of viral particles in the aerosol would contribute to the observed variability. The increase in surface area aorded by these macroporous silica gels would certainly increase the probability of detecting smaller numbers of particles, especially if the sensitivity of the system were increased. The combination of using sol±gel-derived materials as a collector and as a sensor exhibits potential as a fast and ecient mechanism to detect chemicals or organisms in the environment. 5. Conclusions Aerogels are being explored as matrices for biosensors due to a large degree of porosity and extremely large surface area. It has been shown that wetted macroporous silica gel can be integrated as a scaold for bacterial growth and a collector for viral particles. Additionally, immobilized bacterial cells can elicit a measurable response as a result of an environmental trigger. These studies have provided the proof-of-principle that organisms can survive within a wetted mac- roporous silica gel subjected to aerosol exposure and elicit a detectable physiological response to a biological agent within the aerosol. Although, this particular system is only valuable for testing within the laboratory, since the detection of bacteriophage is of no economic value, this model should be transferable to other bioreporter systems. Bacteria with speci®c biological functions could be doped into the gel. For example, the gene for the GFP protein could be cloned behind the promoter for the genes encoding speci®c enzymes for biodegradation of organic pollutants. These organisms could then be immobilized and used to detect these speci®c chemicals in the environment as aerosols, in ground water or in soil. Acknowledgements We would like to acknowledge DARPA and Veridian±PSR for ®nancial support. References [1] M. Uo, K. Yamashita, M. Suzuki, E. Tamiya, I. Karube, A. Makishima, J. Ceram. Soc. Jpn. 100 (1992) 426. [2] R.A. Messing, R.A. Opperman, Biotech. Bioeng. 21 (1979) 49. [3] K. Iwasaki, N. Ueno, J. Ceram. Soc. Jpn, Int. Ed. 98 (1990) 13. [4] H. Kazi, K. Nakanishi, N. Soga, J. Sol±Gel Sci. Technol. 1 (1993) 35. [5] M.C.M. Jaspers, H. Harms, J.R. v.d. Meer, in: R. Fass, Y. Flashner, S. Reuveny (Eds.), Novel Approaches for Bioremediation of Organic Pollution, Kluwer Academic/Plenum, New York, 1999, p. 137. [6] M.E. Power, C.E. Daitch, P.M. Norris, E. Black, J. Gallaher, B. Hosticka, J.F.T. Conroy, Rep. UVA/532567/ MANE99/101, Charlottesville, VA, 1999. [7] E.J.A. Pope, K. Braun, M. Van Hirtum, C.M. Peterson, P. Tresco, J.D. Andrade, in: E. J. A. Pope, S. Sakka, L. Klein (Eds.), Sol±Gel Science and Technology, Ceramic Transactions, vol. 55, American Ceramic Society, Westerville, OH, 1995, p. 33.
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