Open Access Article
Soongwon Cho†
abc,
Michael Brothers†de,
Ziyu Chen†
fg,
Samet Şahin†h,
Yirui Xiong
af,
Nicole Schaeublinde,
Doug Adkinsi,
Charles Callj,
Anthony Banksak,
Steve S. Kim*d and
John A. Rogers
*abflm
aQuerrey Simpson Institute for Bioelectronics, Northwestern University, Evanston, IL 60208, USA. E-mail: jrogers@northwestern.edu
bCenter for Bio-Integrated Electronics, Northwestern University, Evanston, IL 60208, USA
cDepartment of Chemical Engineering, College of Engineering, Kyung Hee University, Yongin, 17104, Republic of Korea
dAir Force Research Laboratory 711th Human Performance Wing, Wright Patterson Air Force Base, Dayton, OH 45432, USA. E-mail: steve.kim.13@us.af.mil
eBlueHalo, 4401 Dayton-Xenia Road, Dayton, OH 45432, USA
fDepartment of Material Science and Engineering, Northwestern University, Evanston, IL 60208, USA
gCollege of Engineering and Computer Science, The Australian National University, Canberra, Australian Capital, Australia
hSchool of Engineering, Lancaster University, Lancaster, LA1 4YW, UK
iDefiant Technologies, 6814 Academy Pkwy W NE, Albuquerque, NM 87109, USA
jBioflyte, 10510 Research Rd SE #100, Albuquerque, NM 87123, USA
kWearifi, 191 Waukegan RD Ste 365, Northfield, IL 60093, USA
lDepartment of Biomedical Engineering, Northwestern University, Evanston, IL 60208, USA
mDepartment of Neurological Surgery, Northwestern University, Evanston, IL 60208, USA
First published on 5th June 2026
Bioaerosols comprise an array of airborne particles that can be benign, contain irritants (i.e., allergens), or disseminate pathogens. Current fieldable devices are incapable of discriminating between benign bioaerosols and pathogenic bioaerosols. Thus, rapid on-site detection and identification at the point of exposure of the components comprising bioaerosols is critical to assess health risks; elimination of both false positives and false negatives is essential to ensure that the correct countermeasures are deployed. The sandwich enzyme-linked immunosorbent assay (sandwich ELISA) remains a gold standard technique for accurate, sensitive detection of proteins, bacteria, and viruses. ELISAs require recognition of the target by two biorecognition elements (BREs) and thus effectively eliminate false positives. The sandwich ELISA, however, suffers from laborious manual processes, which severely impacts its utility in point-of-care (POC). Centrifugal microfluidics offers an automated solution to execute multi-step ELISAs. Here, we introduce a centrifugal microfluidic device that operates based on passive capillary and siphon valving networks to detect human serum albumin (HSA) concentrations in collected bioaerosol samples. We investigate key aspects for minimizing the assay operation time by investigating siphon valve mechanisms, co-incubation time for HSA with a capture antibody and detection antibody conjugated with streptavidin-horse radish peroxidase (strep-HRP), and incubation time for tetramethylbenzidine with strep-HRP for electrochemical amperometric detection. The fully integrated device quantifies HSA concentrations in 15 minutes based on a small sample volume of 12.5 μL. Using the device, we successfully quantify HSA concentrations in bioaerosol samples and obtain results similar to standard 96 well plate-based ELISA.
Bioaerosols are micrometer to nanometer sized airborne particles consisting of a heterogeneous mixture of water, minerals, and biological matter. Bioaerosols can contain one or more of the following: living or dead organisms including bacteria, fungi, and viruses, proteins including biotoxins and pollen, and biomolecules including endotoxins and mycotoxins.2 Their typical concentrations are often observed in ranges of 102–106 colony forming units per m3 for bacteria and fungi3 and 1–2000 grains per m3 for pollen.4
Various natural and artificial sources produce bioaerosols such as microbial degradation, living animals or humans, and human activities or processes.2,5 Inhalation of such toxic or infectious bioaerosols can negatively impact public health and cause allergies, respiratory disorders, inflammation, infection, and acute health issues.2,5–9 However, the threat posed by bioaerosols depends on the components contained within the bioaerosol. Therefore, rapid identification of the bioaerosol components, particularly those that are pathogenic and/or toxic, is required to assess the health risk and inform on the correct mitigation/countermeasures to be deployed. More specifically, rapid on-site detection of toxic and hazardous target analytes within bioaerosols is critical for preventing infectious respiratory diseases, biodefence, and monitoring the exposure risk of workers in occupational environments.10
Unfortunately, reagentless, optical methods, such as Raman spectroscopy,11 to date do not have the requisite specificity to identify toxic agents present in bioaerosols. Therefore, current methods rely on collecting bioaerosols before performing a specific diagnostic test. Aerosol collection often uses a pump to accelerate the bioaerosol particles at a target of interest, either physically entrapping the particles or creating an aerodynamic trap that deposits the larger aerosol particles into a liquid or onto a wall. Collection of bioaerosols12 can be performed either onto a filter, a solid surface (impaction), or into a liquid (impingement), allowing for downstream analysis after transfer using mass spectrometry (MALDI13,14 or ESI15), molecular diagnostics, or immunoassays.
Pathogens, including viruses, bacteria, and fungi, are most accurately and sensitively detected using methods leveraging the polymerase chain reaction (PCR).16 Next-generation detectors can reduce the complexity of devices needed to execute the diagnostic assay using isothermal methods such as loop-mediated isothermal amplification (LAMP) and can use multiple colorimetric17 or fluorometric18 probes to enable multiplexing; however, PCR based methods require DNA/RNA, and are thus limited to organisms. As a result, proteins, including pollen, and small molecules, including endotoxins, must be detected using immunoassays.
Multiple transportable platforms have been developed that enable immunoassays at the point-of-care. Immunoassays can either use a single biorecognition element (BRE) to bind and precipitate the target analyte or two orthogonal BREs to create a sandwich; either platform can then have the binding event correlated with an optical or electrochemical signal. The classical protein immunoassay requires multiple steps to create a signal, consisting of 1) analyte capture and immobilization by a primary, immobilized BRE, 2) washing, 3) analyte binding by a secondary BRE, 4) washing, and 5) signal readout/generation. In some cases, this can be done using a paper matrix, such as for lateral flow assays (LFAs) for proteins including human chorionic gonadotropin (hCG) in pregnancy tests, where the readout can then be reported as a change in absorbance (colorimetric or fluorometric) or reflectance (fluorometric). However, matrix effects are known to cause variability in immunoassay readouts, and thus LFAs can be prone to false positives and negatives19 when the fluid sample changes in composition.
The preferred immunosensor modality is one in which the binding event triggers the sensor change, creating a “reagentless system” and thus enabling continuous use of the sensor. Reagentless optical platforms leverage changes in material surface properties that cause shifts in resonance as a function of mass, such as surface plasmon resonance (SPR) and surface-enhanced Raman spectroscopy (SERS). Reagentless electrochemical based assays include field-effect transistors (FETs), electrochemical aptamer-based sensors (E-AB), and impedimetric sensors that use electrochemical impedance spectroscopy (EIS). However, none of the platforms listed work optimally with antibodies due to the size (large) and rigidity of the capture BRE. Additionally, since these single BRE platforms rely on the affinity and selectivity of a single BRE, identification of alternative BREs that have sufficient affinity and selectivity, including DNA aptamers and peptides, remains a substantial challenge. Table 1 summarizes the pros and cons of current rapid methodologies for detecting specific target analytes in bioaerosols.20 Therefore, the two-BRE system remains the gold-standard, especially when eliminating false positives and negatives, such as for bioaerosol monitoring and biosurveillance, is essential.
| Detection methods | Pros | Cons |
|---|---|---|
| Field effect transistor (FET) immunosensor | Reagentless | Highly sensitive to changes in buffer, salinity, and interferents |
| Rapid response and high sensitivity | Binding events must be close to the surface; typically require a synthetic biorecognition element (BRE) (peptide, aptamer) with significant charge density | |
| Small form factor | A single BRE limits selectivity | |
| Electrochemical aptamer-based sensor (E-AB) immunosensor | Reagent-less | Requires a structure-switching oligonucleotide aptamer modified with a redox mediator (i.e., methylene blue). Few E-AB sensors for proteins exist (NPY,32 thrombin33) |
| Small form factor | A single BRE limits selectivity and limit of detection | |
| Electrochemical impedance spectroscopy (EIS) immunosensor | Rapid response | Complicated electronics and analysis |
| Zero or one reagent needed | Limit of detection and selectivity determined by a single BRE | |
| Small form factor | Works best when the capture BRE is small (synthetic) and the analyte is large | |
| Optical-based immunosensor (surface plasmon resonance (SPR), surface enhanced Raman spectroscopy (SERS)) | Can identify binding as well as quantify underlying binding properties (thermodynamics) | Only use a single BRE, thus may lack selectivity |
| Flow cells and chips can be easily replaced in the field | Fieldable units have reduced/insufficient resolution and sensitivity | |
| Rapid response to analytes | Buffer mismatch can create optical artefacts, especially for real-world samples | |
| Lateral flow assay | Rapid response (<15 minutes) | Relatively low sensitivity (mg mL−1) compared to ELISA (reagent delivery) |
| Easy to use form factor | Device-to-device reproducibility is difficult | |
| Improved specificity using 2 BREs (ELISA) | Quantification struggles when changes exist in the buffer/matrix | |
| ELISA | Highly sensitive (ng mL−1) | Multiple steps require manual processing/time |
| Highly selective using 2 BREs | Assay output takes hours | |
| Minimal background interference | Some outputs require expensive readers |
Among two-BRE sandwich assays, enzyme-linked immunosorbent assay (ELISA), where an enzyme is directly or indirectly attached to the detection BRE, is preferred over direct optical detection because of the amplification of signals that results from the presence of an enzyme reporter. The most common reagent/enzyme combination for ELISA is the use of the enzyme horseradish peroxidase (HRP) coupled to 3,3′,5,5′-tetramethylbenzidine (TMB) in the presence of hydrogen peroxide (H2O2). In short, the HRP couples the reduction of H2O2 to the oxidation of TMB, creating a colorimetric change (clear to blue) that correlates to both the concentration of HRP present (and thus detection antibodies present) and the reaction time. Notably, small concentrations of HRP can result in large colorimetric changes due to the amplification of signals driven by the enzymatic reaction.
However, ELISA also suffers from multiple assay steps with manual operations, laborious washing processes, a long assay time, high cost, and bulky readout equipment.21 Therefore, developing an automated ELISA with rapid readout capability is required for point-of-care monitoring of a specific target analyte within bioaerosols.22,23 Centrifugal microfluidics, operating based on centrifugal force, offer solutions for automating multiple sequences of ELISA including reagent incubation, washing, mixing, and sequential addition of reagents.22,24,25 Enhanced mixing processes enable rapid detection of target analytes based on minimal sample volume (<15 μL) within 15 minutes.26,27 Table 2 summarizes recent advances in centrifugal microfluidic platforms for immunoassay and demonstrates that our platform is comparable to the current state-of-the-art platforms in terms of its detection time, reagent volume, fully passive mode of operation, and sensitivity, while noting that direct comparison of limits of detection depends on the target biomarker, antibody pair, and assay chemistry.
| Parameters | Lab-on-a-disc for fully integrated ELISA | Flow-enhanced electrochemical immunosensors | Lab in a bento box | This paper |
|---|---|---|---|---|
| Published | 2012 | 2013 | 2020 | 2026 |
| Sample matrix | Whole blood | DPBS | DPBS | Bioaerosol |
| Fluidic control | Active | Active | Passive | Passive |
| (Wax valve with laser) | (Wax valve with laser) | (Centrifugal hydrokinetics) | (Capillary/siphon) | |
| Throughput | 3 | 3 | 2 | 3 |
| Target biomarker | C-reactive protein | C-reactive protein | Mouse IgG | Human serum albumin |
| Cardiac troponin I | ||||
| N-terminal | ||||
| Pro-B type natriuretic peptide | ||||
| Detection time | 20 minutes | 20 minutes | 12 minutes | 15 minutes |
| Sample volume | 66 μL | 75 μL | 30 μL | 12.5 μL |
| Detection antibody | 66 μL | 75 μL | 12.5 μL | |
| Washing volume | 116 μL | 200 μL | 150 μL | 60 μL |
| TMB volume | 100 μL | 110 μL | 40 μL | 30 μL |
| Limit of detection | 0.27/0.46/0.34 ng mL−1 | 4.9 pg mL−1 | 0.76 ng mL−1 | 4.2 ng mL−1 |
| Detection | Optical | Electrochemical | Optical | Electrochemical |
| Reference | 24 | 22 | 26 | This work |
Here, we introduce a centrifugal microfluidic platform based on passive capillary and siphon valving networks for an automated ELISA after manual sample loading. Human serum albumin (HSA) was used as a model target analyte, as its size (66.5 kDa) is comparable to pollen,28 protein biotoxins,29 and other protein targets of interest. First, we demonstrate the capabilities of performing fluidic operations entirely based on centrifugal force without active actuation. We then investigate key components of the device for minimizing the assay time including siphon valves, co-incubation time for HSA with capture and detection antibodies, and TMB incubation time with HRP enzymes. Through these optimizations, the device successfully detects HSA concentrations in collected bioaerosol samples (12.5 μL) within 15 minutes with sensitivity comparable to that of plate ELISA.
The device consists of four components (Fig. 1b, left): a slab of polydimethylsiloxane (PDMS) with relief structures that define channels and chambers (microfluidic layer), a synthetic pressure sensitive adhesive (PSA) with CO2 laser-cut microfluidic chambers, a bottom substrate of polymethyl methacrylate (PMMA), and gold electrodes on a glass substrate. These layers bond together to create a series of reservoirs that can be modified to enable fluidic movement, and thus operation of an ELISA (Fig. 1b, middle). The input for this lab-on-a-CD consists of bioaerosols collected using a sampler, such as the handheld Biocapture 650 (Fig. 1b, right), that captures airborne particles using a rotating impactor into a water-based collection fluid. Fig. 1c and d show the assembled device and with food dyes loaded into each chamber for visualization, respectively. The image of the bioaerosol collector is shown in Fig. 1e, with the ability to concentrate bioaerosols into small volumes that can be processed by the lab-on-a-CD ELISA.
Fig. 1e shows the bioaerosol sample collection instrumentation, which operates as a separate upstream module from the centrifugal microfluidic device and concentrates bioaerosols into small liquid volumes for subsequent centrifugal microfluidic ELISA analysis. The collector consists of an aerosol sample intake inlet adjacent to a single-stage axial impactor milled out of stainless steel plates. The impactor pulls air through the aerosol sample intake and through the spotting nozzle into a sample cup, where an aerodynamic trap causes deposition of bioaerosols in the sample cup. This cup connects to two peristaltic pumps and a series of three-way valves to enable fluid flow in and out to 1) resolubilize the collected bioaerosol in the buffer from the reservoir, 2) move the fluid from the cup into the sample vial, 3) rinse the cup with reservoir buffer and 4) move the waste wash into the waste wash reservoir. This process allows for automated collection of bioaerosols into a buffered solution compatible with bioassays as well as regeneration of the collection system.
In step 1, the capture antibody conjugated polystyrene (PS) beads co-incubate with HSA, biotinylated detection antibody, and strep-HRP. During co-incubation, HSA binds to the capture antibodies on the PS beads, while the biotinylated detection antibody binds to bead captured HSA to form the sandwich immunocomplex. Strep-HRP then associates with the biotinylated detection antibody and serves as the enzymatic label for subsequent TMB oxidation and electrochemical detection. The PS beads serve as the solid phase support for target capture, analogous to the antibody coated surface in a conventional well plate ELISA, while enabling efficient mixing during centrifugal operation. In step 2, the washing step removes any unbound HSA, biotinylated detection antibody, and strep-HRP from the chamber. In step 3, bead bound strep-HRP oxidizes TMB. In step 4, gold electrodes detect the oxidized TMB species by producing amperometric signals proportional to HSA concentrations.
The corresponding device configuration, detailed valve numbering, burst frequencies, and spin protocol are shown in Fig. 2b and c and Table 3. As shown in Fig. 2b, the device consists of a series of chambers for loading and processing assay reagents. Specifically, the reagent chamber contains the bioaerosol sample, biotinylated detection antibody, and strep-HRP for the protein binding reaction. The reaction chamber at the center of the device contains PS beads, where the ELISA reactions occur. The selected bead size balances the capture surface area, mixing efficiency, and reliable retention within the reaction chamber during centrifugal operation. Smaller beads can provide a larger effective surface area and accelerate binding kinetics by minimizing the distance needed for analyte/reagent diffusion.30 Bead transport and retention during centrifugal washing also depend, however, on particle size. Stokes-type sedimentation in centrifugal microfluidic systems scales with bead radius squared. As a result, further reductions in bead size may require increased rotational frequencies or spin times for stable retention,31 with additional risks of clogging the capillary valves during operation. The number of the valves corresponds to their order of operation during the automated assay sequence. Careful design of the geometry and burst frequency of each valve allows selective actuation of the required valves at specific rotational frequencies during the spin protocol, while the remaining valves remain closed until their designated operation steps, as summarized in Fig. 2c and Table 3.
| Step | Description | Frequency (Hz) | Time (s) | Activated valves |
|---|---|---|---|---|
| 1 | Conjugation | 14 | 20 | 1 |
| Mixing | ±5 | 180 | ||
| 2 | First washing | 60 | 90 | 2, 3, 4, 5 |
| 3 | Second washing | 2 | 60 | |
| 14 | 5 | 6 | ||
| 10 | 60 | 6 | ||
| Mixing | ±5 | 30 | ||
| 4 | 60 | 90 | 2, 8, 9 | |
| 5 | TMB substrate reaction | 2 | 60 | |
| 14 | 5 | 10 | ||
| 10 | 60 | 10 | ||
| Mixing | ±5 | 180 | ||
| 6 | TMB detection | 25 | 5 | 7 |
| 2 | 60 | |||
| 7 | 14 | 20 | 11 |
The oxidized TMB/H2O2 substrate solution passes to the chamber for amperometric detection via a series of spin controls (Fig. 3i). The siphon valve from the reaction chamber to the detection chamber is activated by spinning the disc at 25 Hz for 5 seconds. Spinning at 2 Hz for 60 seconds primes the siphon valve. Rotation at 14 Hz for 20 seconds transfers the sample to the detection chamber. A demonstration of the automated fluidic process appears in Video S1.
| Parameters | Conventional planar 96 well plate HSA ELISA | This work | |
|---|---|---|---|
| Assay format | Format | 96 well-plate planar sandwich ELISA | Bead-based sandwich ELISA |
| Capture support | Antibody coated well-plate surface | Antibody conjugated PS beads | |
| Operation | Manual pipetting | Automated centrifugal microfluidics | |
| Detection method | Optical | Electrochemical | |
| Assay preparation | ① Bioaerosol collector | 10 minutes | 10 minutes |
| ② Sample loading | 2 minutes | 2 minutes | |
| Assay time | ③ Fluidics/operation | 10 minutes | 4 minutes |
| ④ Protein binding | 2 hours | 3 minutes | |
| ⑤ Washing | 30 minutes | 5 minutes | |
| ⑥ TMB oxidation | 20 minutes | 3 minutes | |
| Total | 3 hours 12 minutes | 27 minutes | |
| Reagent volume | Sample volume | 100 μL | 12.5 μL |
| Limit of detection | 2.5 ng mL−1 | 4.2 ng mL−1 | |
Optimizing the siphon valve is crucial for reducing the time required for fluid operation. The time for fluids to travel through the hydrophilic siphon microchannel can vary from 1 minute to more than 4 minutes depending on the characteristics of the PVA coating. Measurements of this priming time involve observations of the times required for the fluid to reach the crest and the full length of the siphon valve after bursting capillary valve 1 (Fig. 4a). Increasing the concentration of PVA on the microchannel decreases the rate of the capillary hydrophilic wicking process due to the reduced rate of PVA dissolution at the moving liquid front (Fig. 4b and c). Fig. 4d and e display the dynamic change in the contact angle of a water droplet on a PDMS surface coated with a thin film of PVA. The contact angle decreases gradually over time due to the slow dissolution of PVA in the water at high PVA concentration which is consistent with observations of the siphon valve priming time. We evaluated the effect of temperature on siphon priming time because PVA dissolution and liquid viscosity can depend on ambient temperature. Siphon priming time decreased with increasing temperature, from approximately 46 s at 0 °C to 29 s at 20 °C and 19 s at 40 °C (Fig. S5). Although temperature affected valve timing, the siphon primed within less than 1 min across the tested range, indicating that the current spin protocol provides sufficient timing margin for valve operation.
Detailed investigations reveal that an incubation time of 3 minutes for both step 1 (HSA co-incubation) and step 3 (TMB oxidation) is sufficient to generate a detectable signal for HSA at a concentration of 80 ng mL−1 (Fig. 5a and b). The saturation behavior of the measured charge signal defined the criterion for selecting each incubation time. Three minutes correspond to the time beyond which the rate of change in charge drops below a threshold value. After this time, continued incubation produces negligible signal gain relative to measurement variability. This response follows from the large surface area of the PS beads, together with an effective centrifugal mixing process based on optimized spin protocols. Owing to the digitally controlled spin protocol, the actual timing error in practice is on the order of 1 second or less. Even under a conservative assumption of a ±5 second deviation, the resulting variation in the measured signal remains within ±2.5% for protein binding and ±0.4% for TMB oxidation, confirming that the assay is insensitive to minor timing fluctuations. A standard calibration curve based on 3 minute incubation time reveals a limit of detection (LOD) of 4.2 ng mL−1 and a linear range of 10 to 160 ng mL−1 with a correlation coefficient of 0.99 (Fig. 5c). This value is comparable to the lower assay range of the conventional HSA Duoset ELISA, 2.5 ng mL−1, while using a substantially shorter assay time. Further improvements in LOD may be possible by optimizing bead loading, incubation conditions, and electrochemical signal amplification. The corresponding chronoamperometric responses for the standard calibration curve are shown in Fig. 5d. This assay can be conducted on volumes as small as 12.5 μL, compatible with short bioaerosol collection times. Fig. 5e illustrates the use of peristaltic pumps and valves to move the resolubilization buffer into and out of the sample cup containing the bioaerosol. Notably, valve operation allows the buffer from the liquid reservoir or a separate rinsing reservoir to 1) resuspend the protein bioaerosol for analysis, 2) agitate by vibration and/or fluid pumping, 3) transfer the collected bioaerosol to the device for analysis and 4) wash the sample cup before subsequent bioaerosol collections. Detailed collection times and volumes during sample rinsing and washing steps are included in Table S1. Fig. 5f demonstrates the ability to estimate HSA concentrations in collected bioaerosol samples, with comparisons to results obtained with standard plate ELISA methods. To enable quantitation within the lab-on-a-CD, collected bioaerosol samples are diluted 16 times before use in both plate and centrifugal microfluidic ELISAs. The estimated HSA concentrations of these diluted bioaerosol samples are 84.3 ng mL−1 and 82.1 ng mL−1 for centrifugal microfluidics and plate ELISA, respectively.
Notably, we illustrate that the device can detect the proteins from the bioaerosol by operating a rapid ELISA. The collected bioaerosol sample is then injected into the device for the quantification of HSA within 15 minutes. Optimization of microfluidic siphon valves, co-incubation time of reagents, and TMB reaction time with strep-HRP enzymes enables rapid HSA quantification. A lower concentration of hydrophilic PVA coating on the microchannels facilitates the liquid priming process which leads to faster priming speed for the siphon valve. This allows the entire microfluidic process to be completed within 4 minutes. Enhanced mixing processes within the device ensure successful HSA quantification with 3 minutes of co-incubation time for all assay reagents, and 3 minutes for the TMB/H2O2 reaction. Application of the system for detecting HSA concentrations in collected bioaerosol samples demonstrates excellent performance, as validated by gold standard well plate-based ELISA. Initial experiments using AuNPs as model particulate interferents show limited effects on HRP-mediated TMB electrochemical detection and indicate that BSA blocking can reduce particle associated non-specific background. Comprehensive testing with diverse real-world environmental matrices remains an important future direction for field deployability. Other biotoxins or infectious agents can be detected by modifying the platform described here, mainly by swapping out the detection and capture antibodies to enable selective detection of the target analyte; the bioaerosol collector may need to be modified to use liquid impingement to preserve the protein tertiary structure, but otherwise the device from bioaerosol collection to analysis should require minimal changes. Thus, we expect that the technologies introduced here offer a platform for rapid collection and detection of toxic and infectious bioaerosols that will enable improved implementation of countermeasures to reduce the spread of infectious agents, including deployment of quarantines and therapeutics to proactively treat individuals exposed to toxic bioaerosols.
| Substrate material | Microfluidic device | Bonding | Pros | Cons |
|---|---|---|---|---|
| PMMA | PDMS | Oxygen plasma | Simple fabrication | Weak bonding |
| PMMA | PDMS | Oxygen plasma | Strong bonding | Chemical treatment |
| (3-Aminopropyl)triethoxysilane | Surface functionalization | |||
| Tetraethyl orthosilicate | ||||
| PMMA | PDMS | Thin uncured PDMS | Simple fabrication | Weak bonding |
| PDMS | PDMS | Oxygen plasma | Simple fabrication | Weak bonding |
| Too flexible for spinning | ||||
| Glass | PDMS | Oxygen plasma | Strong bonding | Glass fragility, safety |
| Glass machining | ||||
| Silicon wafer | PDMS | Oxygen plasma | Strong bonding | Cost of fabrication |
| Surface properties | ||||
| PMMA | PDMS | Rubber-based pressure sensitive adhesive | Strong bonding | — |
| (This work) | Rapid prototyping | |||
| Low cost | ||||
| Microstructures (<30 μm) of multiple levels of depth |
Fabrication of the molds began by defining iron oxide photomasks with a pre-coated AZ1518 photoresist (Nanofilm) using an MLA 150 Maskless aligner (Heidelberg Instruments) with exposure conditions of 375 nm wavelength and 55 mJ cm−2 dose. Developing with a 1
:
4 mixture of AZ400K developer (IMM integrated micro materials) and deionized water for 60 seconds exposed the iron oxide layer to allow its patterned removal by etching with ME-9028 (Transene) for 30 seconds. Stripping the residual photoresist by immersion in acetone completed the fabrication of the photomask. Three iron oxide masks were created for different microfluidic thicknesses of 30, 100, and 400 μm.
Preparation of the 4 inch wafer (Universal wafer) began by cleaning with isopropyl alcohol and deionized water and baking on a hot plate at 95 °C for 10 minutes. Plasma treatment (PC300, Samco) at 100 watts for 30 minutes facilitated strong adhesion of SU-8 coatings formed by spin-casting onto the hydrophilic silicon wafer surface. A uniform base layer SU-8 2005 with a 10 μm thickness formed by casting and flood exposure promoted strong adhesion of subsequent SU-8 layers created by multi-layer photolithographic processes consisting of spin-coating, edge bead removal, pre-baking, aligned UV exposure, and post-baking steps. Developing the wafer with the SU-8 developer for 1 hour defined the SU-8 microstructures for molding of the PDMS microfluidic layer. A surface coating of perfluorooctyl trichlorosilane by vapor phase deposition rendered the surface hydrophobic and facilitated the removal of PDMS from the surface of the wafer after curing.
:
1 ratio) on a wafer and curing it on a hot plate at 95 °C for 30 minutes produced 0.8 mm thick layers of PDMS. Rendering the PDMS surface hydrophilic by plasma treatment (PC2000, South Bay Technology) at 100 watts for 30 minutes allowed for local coating of PVA within the microchannels. The hydrophilic surface enabled the PVA solution (1 μL, 0.05% w/w) to spread evenly across the microchannels of the siphon valve upon drop-casting and subsequent drying at room temperature for 30 minutes. A set of mechanical hole punches created inlet holes, vent holes, and rotational center holes for each PDMS microfluidic layer.
Designs for PSA and PMMA layers were prepared in AutoCAD software (Autodesk) and cut using a VLS CO2 laser (Universal Laser Systems). A CO2 laser system patterned microfluidic chambers with ±254 μm resolution. Soft lithographic processes were used for capillary valves with dimensions smaller than 100 μm. A custom alignment JIG with three pogo pins allowed bonding of the PMMA and PSA layers with a ±200 μm alignment margin. A hard rubber brayer roller (Speedball) ensured tight contact between layers. PMMA/PSA layers served as a substrate for bonding to the PDMS microfluidic layer. Subsequent exposure to a corona discharge activated both surfaces for bonding, with the same JIG for alignment. The device was then baked in an oven at 75 °C for 2 hours to recover hydrophobicity. Placement of electrodes on the detection chamber completed the assembly process.
:
3 ratio. The photoresist cocktail was then spin-coated onto a glass substrate (75 mm × 50 mm) at 3000 rpm for 30 seconds, followed by a prebake step at 110 °C for 2 minutes. Subsequent exposure to UV light (375 nm, MJB4 mask aligner, Suss Microtec) for 20 seconds and development of the exposed substrate with AZ 300 K developer for 120 seconds created the electrode patterns, preparing the substrate for deposition of 10 nm of chromium and 100 nm of gold layers at a rate of 1 angstrom per second on the photoresist-patterned glass slide using an electron beam evaporator (AJA International). After metal deposition, immersing the glass slide in an acetone bath stripped the AZ 10XT photoresist from the glass slide along with the chromium and gold layers deposited on top of it. The resulting pattern consisted of working (2 mm circle), counter, and reference gold electrodes for the electrochemical detection of the oxidized TMB substrate.
Bioaerosols were collected at 2 LPM through a single-stage axial impaction using a spotting nozzle (15 mils) to focus the bioaerosol into a collection cup. After collection (10 minutes), a Tris buffer (10 mM Tris, pH 7.5, 0.05% Tween-20) was added to the collection cup to dilute and resuspend the collected bioaerosol from the spotting nozzle into 100 μL of buffer. The solution, once in the spotting nozzle, was agitated using a vibrating motor and heated to a moderate temperature (∼37 °C) to improve the solubilization of the protein. For a five-minute collection time, a maximum of ∼20 μg could be collected and solubilized into 100 μL of buffer.
Supplementary information (SI) is available. See DOI: https://doi.org/10.1039/d6lc00061d.
The views expressed are those of the authors and do not reflect the official guidance or position of the United States Government, the Department of Defense, or of the United States Air Force. Appearance of, or reference to, any commercial products or services does not constitute DoD endorsement of those products or services. Imagery in this document were produced by the authors.
Footnote |
| † These authors contributed equally to this work. |
| This journal is © The Royal Society of Chemistry 2026 |