Open Access Article
Ellinor Hedberg
a,
Jaime Sebastián-Azconab,
Federico Ribet
a,
Virginia Hernandez-Santanab,
Göran Stemme
a,
Antonio Diaz Espejob and
Niclas Roxhed*ac
aDepartment of Micro and Nanosystems, KTH Royal Institute of Technology, Stockholm, Sweden. E-mail: roxhed@kth.se
bPlant Ecophysiology and Irrigation Group, Instituto de Recursos Naturales y Agrobiología de Sevilla (IRNAS, CSIC), Sevilla, Spain
cMedTechLabs, Karolinska University Hospital, Solna, Sweden
First published on 24th April 2026
Plant sap analysis typically relies on destructive sampling and immediate freezing, limiting field deployment and longitudinal studies. We introduce a minimally invasive microfluidic device that extracts sap from the stem of Solanum lycopersicum and dries it in situ, enabling storage analogous to dried blood spots in humans. Using both artificial phytohormone mixtures and tomato sap, we assessed the stability of dried samples stored at room temperature for up to seven days and observed no substantial degradation of key phytohormones. Device performance was further validated in a paired sampling experiment, showing strong agreement with a conventional stem severing method for tZR and ABA quantification. These findings demonstrate that dried sap sampling via a microfluidic device provides a practical, field ready alternative to destructive methods, supporting repeated sampling from the same plant and enabling longitudinal metabolic monitoring.
When collecting samples for phytohormonal or metabolomic analysis, the sampling strategy and subsequent handling are critical determinants of the quality of the obtained results.5 Several conventional approaches are used to extract plant sap, with the choice depending both on the plant species and the sap type of interest. Examples include pressing/crushing tissue,6 making incisions in self-bleeding plants, applying EDTA treatments to prevent sieve element blockage by P-proteins,3 aphid stylectomy to extract pure phloem sap,7 centrifugation8 or application of external pressure.9,10
In collected samples, enzymes can cause degradation of metabolites or other analytes of interest. To prevent this, the standard approach is to freeze the sample, thereby halting the enzymatic activity. Freezing can be achieved through lyophilization (freeze-drying) or by using liquid nitrogen (fresh-frozen).11–14 An alternative approach has been suggested, which involves drying samples at room temperature. For example, cornflower petals subjected to this method exhibited low water activity, a parameter closely related to enzymatic activity, compared to hot-air convective drying and lyophilization.15–17 Equally important as sample collection are the subsequent storage and transport conditions, which must be carefully controlled to ensure sample stability.5,12,14 Successful metabolomic analysis requires an optimized protocol for sample collection, a reproducible sampling procedure, and robust transport and storage conditions.
Inspired by human sampling, dried blood spot (DBS) microsampling has become a common procedure for easy blood sample collection and long-term storage. Due to the low enzymatic activity in dried samples, proteins can remain stable for up to 30 years with minimal destruction of the analyte and only minor changes in detection levels.18–20 Hormones21 and metabolites22 have also been successfully analysed in DBS samples, with hormones shown to remain stable for four weeks at room temperature and up to a year in cold storage.21
Thus, DBS enables easy sampling procedures without greatly compromising the analyte integrity. Given that plant sap functions as the transport medium for phytohormones and metabolites in a manner that could be seen as somewhat analogous to the human blood stream, we hypothesize that a paper-based drying approach could be applied to plant sap for the analysis of phytohormones.
Here we show a microsampling device that combines the approach of drying plant sap samples in room temperature, similar to the approach of DBS, using a sampling procedure that allows for sample collection in a more low-invasive manner compared to conventional approaches. The microsampling device consists of a microfluidic channel connected to a paper matrix enclosed in a plastic case. This configuration allows for quick and easy sap sampling, with minimal manual intervention, and with integrated sample drying inside the plastic casing through a vent.
588 Sigma-Aldrich), trans-zeatin riboside (tZR) (6025-53-2 Olchemim) and jasmonic acid (JA) (3572-66-5 Olchemim) were used to evaluate the PHM stability upon drying. The phytohormones were mixed to make a solution with concentrations determined from a preliminary experiment. In the preliminary experiments the microfluidic device was evaluated to determine if phytohormones could be detected in a sap sample stored in a paper matrix, and in what concentrations. From the evaluated phytohormones, IAA, SA, ABA, tZR and JA were determined to be the ones with the most relevance for these experiments as well as showing good detectability. The concentrations for each of the phytohormones were selected based on the concentration they had in the preliminary study multiplied with a factor of five to ensure good readings away from limit-of-detection.
The selected phytohormones were mixed to their determined concentrations (IAA 0.05 pmol μL−1, ABA 0.5 pmol μL−1, SA 0.5 pmol μL−1, tZR 0.5 pmol μL−1 and JA 0.5 pmol μL−1), and 7 μL of the PHM was pipetted onto Sartorius 601-N filter paper with dimensions (5.5 mm, 8.5 mm, 0.19 mm), same as the papers in the microfluidic device. Five of the paper pieces were immediately placed in Eppendorf tubes and stored at −80 °C until analysis. The rest were left in room temperature for drying for 20 min, 140 min, 5 h, 24 h and 7 days. The PHM and the individual phytohormone components were stored in −80 °C and 4 °C for 10 days to compare their stability in liquid form over time, Fig. S1.
As a biological comparison to the PHM samples, the cultivated tomato plants were sampled by insertion of the microfluidic device into the stem. The sampling was made at the fourth node from the top of the plant, and this was the same for all the plants where possible. If not possible, for example due to the shape of the plant and the size of the stem at that location, sampling was done as close to that point as possible. Once filled, the devices were removed from the stems and left at room temperature for the same time intervals as the artificial phytohormone samples. The storage paper was removed from the device and placed in an Eppendorf tube prior to storage at −80 °C until further analysis. Three tomato plants were also sampled using a stem severing method in which a piece of the stem was cut and placed in an Eppendorf tube followed by centrifugation in a table top centrifuge to extract sap. The collected sap was stored in liquid form at −80 °C until analysis.
36 tomato plants (Solanum lycopersicum, Tres Cantos) were placed in a greenhouse with temperature and humidity controls (HC2S3, Campbell Scientific) and plant lights (The Jackson Nemesis 250 W, The Jungle) to ensure good growth conditions. Plants were placed in methacrylate boxes with dimensions 34 × 37 × 57 cm3 to ensure controlled environments. The plants were sampled at three different time points with five replicates over four days (exception at three time points where three or four plants were sampled instead of five), creating a total of 72 samples. The sampling was carried out by first using the microfluidic sampling device followed by destructive sampling of cutting a piece of the plant for sap extraction close to the sampling site from the device. This to keep the samples as similar as possible. Approximately 8 cm of the stem was cut from the plant close to the incision site of the device. The plant section was placed in liquid nitrogen and the frozen plant samples were placed in Eppendorf tubes and spun in a tabletop centrifuge (for 60–75 seconds) at 12
000 rpm. The liquid obtained was aspirated and 7 μL placed on the same paper matrix as in the devices used for the microfluidic sampling. These samples were then placed in −80 °C. The microfluidic samples were collected by inserting the needle at the second node of the plant from the top, and once the devices had filled with liquid they were opened and the storage paper was placed in an Eppendorf tube and stored in −80 °C until analysis. Fig. 1G shows a schematic overview of the sampling process.
The volumes extracted with the microfluidic sampling devices varied as indicated in the metadata, (SI), where the collected volume was determined by visual inspection and comparison to the calibration experiment with devices filled with known volumes to indicate the filling, Fig. 1D. The volumes have been accounted for in the analysis by normalizing to the collected volume range.
The drying times for the storage paper in the microfluidic devices when evaluated with DI water are presented in Fig. 1F and S4. The averge evaporation rate is 0.05 μL min−1 for all devices. The first 20 minutes show a clear non-linear behaviour, this corresponds to evaporation of water that has adhered to the surface of the device when filling and potentially evaporation from the inlet channel. The linear range, where the evaporation rate is calculated, corresponds to evaporation from the storage paper matrix. This means that on average it takes approximately 2 hours for the devices to dry.
Extraction of the sap samples from the storage paper was done using the following protocol. 400 μL ice cold 60% acetonitrile (ACN) and 2 μL of isotopically labeled internal standard mix was added to the samples followed by shaking in mixer mill at 30 Hz for 10 min. The samples were then centrifuged at 14
000 rpm for 10 min at 4 °C. After centrifugation, 350 μL of the supernatant was transferred to new vials and dried using speedvac at 40 °C for 1 h, followed by room temperature for 1 h and storage overnight at −70 °C. The samples were dissolved in 43 μL 20% acetonitrile and 10 μL was analyzed with UHPLC-QQQ-MS/MS, a 1290 Infinity Binary LC System coupled to a 6495 Triple Quad LC/MS System with Jet Stream and Dual Ion Funnel technologies (Agilent Technologies). Metabolite separation was performed with a Acquity UPLC CSH C18 RP column (150 × 2.1 mm, particle size of 1.7 μm), with a column temperature of 40 °C, and a flow rate of 0.25 mL min−1. The mobile phases were A: 0.01% formic acid in Milli-Q H2O, and B: 0.01% formic acid in 100% acetonitrile. The quantification was carried out in Agilent MassHunter Workstation Software Quantitative (Agilent Technologies). Solvents used: methanol, HPLC-grade was obtained from Fischer Scientific, and acetonitrile, hypergrade for LC-MS LiChrosolv was obtained from Merck.28
The storage paper holds a maximum of 7 μL, the remaining 0.5 μL is the volume of the needle/capillary channel and an additional 0.5 μL which collects around the edges of the storage paper in the collection chamber. The volume collected in the storage paper can be visually determined by observing the liquid filling and the corresponding colour shift in the wetted paper matrix. If the sampled plant does not have a lot of readily available sap, enabling a fully filled device, the visual indication of the colour shift can be used to determine the collected volume. The accuracy of the device was determined using gravimetric measurements combined with visual observation of volume filling, Fig. 1D and E. At volumes above 5 μL the device reaches saturation, meaning that the collected volumes cannot be reliably separated from one another. At lower volumes the spread through wetting of the paper can cause greater spans of visually observed filling for the same volume. To account for these variations, a min/max approach has been taken for the analysis where the curve presented in Fig. 1D has been used to define a max, min, and average volume collected, Fig. S2 presents the detected phytohormonal concentrations with error bars indicating the max and min concentrations in this range. Additionally, a gravimetric evaluation was conducted through collection of sap visually indicating 100% filling, i.e. a volume range of 4.5–8 μL. By gravimetric evaluation of the collected mass, it could be determined that the average mass collected was 5.4 mg, with a standard deviation of 0.87 mg. This corresponds to a coefficient of variation of approximately 16%, Fig. 1E. For the pipetted volumes the CV% varies from approximately 30% for the greatest distributions at 1–2 μL down to 0% for the largest volumes that are always accurately recorded as fully filled, Fig. S3.
The destructive samples collected from tomato plants through centrifugation at time point 0 min presented concentrations similar to the device samples. Although the 0 min destructive samples do not always display similar concentrations as the 0 min device sample counterpart for all the phytohormones, the destructive samples remain within the expected range when looking at all samples combined.
The phytohormone tZR, Fig. 2Ai and ii, is relatively stable over time, with no major deviations observed over the evaluated days, indicating that the phytohormone can be reliably dried and stored in paper.
IAA present a large drop in concentration after the first 20 min in the plant sap sample, Fig. 2Aiv, this can in part be attributed to the high variability of the concentrations at sampling time 0 min. The distribution of IAA concentrations are similar from 140 min to 24 h for all triplicates. However, the greater variability compared at time points 0 min and 20 min, indicates that the IAA concentrations vary quite a lot between individual plant samples. Since the same effect cannot be seen in the artificial PHM, Fig. 2Aiii, this could be attributed to individual differences between plants or potentially enzymatic effects in the plant sap, degrading the endogenous plant sample while not showing the same effects in the artificial counterpart. Since the drying time for the devices is approximately 2 hours, this correlate with the observation that IAA concentrations vary more before this timepoint and is reduced after when the enzymatic effect should be lower.
ABA concentrations show a main deviating sample at time point 0 min for the plant sap samples, Fig. 2Avi. There is variability seen in most ABA sap samples, but they are quite consistent although more dispersed than in the PHM samples.
SA shows more fluctuating concentrations in the sap samples, and the increase at 24 h and 7 days indicates variability in the stability of the phytohormone and/or individual differences between plants, Fig. 2Aviii. In the PHM, differences can be observed for SA that indicate issues with fully dissolving the phytohormone, leading to greater variations between samples, Fig. 2Avii.
36 plants were sampled over four days. First, the microfluidic sampling device was used, followed by cutting a piece of the plant close to the microdevice sampling site to keep the samples as similar as possible. By obtaining a paired measurement from the same plant using both these methods, we could compare the sampling methodologies and evaluate the accuracy of the sampler. In the pairwise comparison, Fig. 2D, the destructive samples are generally higher in concentration compared to the microfluidic device samples.
For tZR, high concentrations of the destructive samples correspond with high concentrations from the microsampler and vice versa, with similar values across both methods, Fig. 2Di. IAA show greater variability for the sampling methods and not a clear pattern between the high vs. low measurements from the two approaches, Fig. 2Dii. ABA display a clear difference where destructive samples are consistently higher in concentration than their microfluidic counterpart, Fig. 2Diii. However, the pairs correlate with high destructive sample concentrations pairing with the higher device concentrations. The variability of the SA samples is greater than that of the ABA and tZR samples, and more similar to IAA. The destructive samples are generally higher in concentration than the microfluidic device samples but the correlation between high and low values between the sampling approaches is not as prominent as for ABA, Fig. 2Div.
To further compare the two sampling procedures, a Bland Altman analysis and a linear regression correlation analysis were conducted, Fig. 2B and C. The Bland–Altman analysis was conducted through a pairwise comparison of the destructive method as control with the microfluidic device sampling approach as the comparative method. The destructive and device samples were taken as pairs, therefore the comparison reduce potential errors that can arise from two different individuals and rather only evaluates the sampling approach, Fig. 2C.
The Bland–Altman analysis clearly display that both ABA and SA show a bias in favour of the destructive method, as was also observed in Fig. 2D where the concentrations from the destructive sampling are generally higher than the device sample concentrations. However, the samples (except for two points for ABA and one for SA) are within the 95% CI in Fig. 2Ciii and iv. With the knowledge of the under-representation of the device for these phytohormones, appropriate adjustments could be made to create a standard curve for determination of the concentrations from the microfluidic device. In Fig. 2B, the correlation analysis show ABA samples following a linear distribution (p < 0.0001), with no evidence of deviation from linearity (runs test p = 0.44), compared to SA where no clear correlation (p = 0.545) can be seen. For tZR the linear regression analysis revealed a linear relationship between destructive and device samples (p < 0.0001), and no evidence of deviation from linearity (runs test p = 0.21). IAA show a negative linear relationship (p = 0.014), however a low R2 indicates weak associations, this introduces complexity in attempting to create a conversion factor between the two approaches, Fig. 2Ci and ii. Thus, ABA and tZR appear to be the two phytohormones that provide the most accurate concentrations from the microfluidic sampler when compared to the destructive sampling approach.
The degree of similarity when comparing the destructive stem severing approach to the microfluidic sampler, varies between the tested phytohormones. Some phytohormonal concentrations are underrepresented in the sampling device (ABA and SA) whereas others show similar concentrations using both approaches (tZR and IAA) but with no clear pattern between high and low concentrations (IAA and SA). The trend observed for all phytohormones excluding IAA, is that their concentrations can be translated between the sampler and the control method to some degree, where tZR and ABA present the most consistent relationships to enable such conversions. To enable a good use of the microfluidic sampler, a conversion factor or standard curve should be developed that can be used to translate a detected concentration in the microfluidic sampler to the concentration as detected in the destructive samples.
The main limitation of the microfluidic sampler is the variability in the collected volume. To address this, modifications to the design are required to increase accuracy in the collected volume and thus the concentrations in the dried paper matrix. For example, a different storage paper could be used that can absorb larger quantities of sap and thereby make clearer distinctions about visual filling of different volumes. The length of the device can be extended to allow for a larger wicking area and thus provide the same benefit as a different material selection. Introducing a metering capability to ensure that a specific volume is always collected could be implemented, with the limitation of biological variance between different plant individuals. Some plant individuals allow for the extraction of large volumes (up to 15 μL) whereas others only allow for 1–2 μL. By having a set metering capability, the variability would be significantly reduced, but the number of samples collected would be reduced as well. Potentially a combination could be envisioned as the best approach where volumes below a certain limit can be visually determined and a metering capability that has a cut-off at the defined highest volume extraction.
Future evaluations should also consider the aspect of in-field sampling in different environments, such as tropical settings or greenhouses with high humidity that would affect the drying process and thereby potentially cause degradation of analytes. The drying time in a laboratory environment is observed to be on average 2 hours. With increasing humidity this can be expected to increase as well. The drying speed of DBS has been shown to depend on the relative humidity (RH) of the surrounding environment, and the analyte distribution is altered based on RH, leading to a reduced homogeneity.29 It can therefore be expected that a similar effect would occur for the sap samples drying in environments with increased RHs. To what extent and what analytes are affected is a highly relevant and natural extension for future validations of this device for usability in real life environments.
The device presents new opportunities for longitudinal monitoring of plants over time, an approach that has had major successes in both health care and patient centric sampling settings for humans. Underlying patterns of disease have been discovered, and new understandings of human physiology and potential inter-individual variability has been gained.30,31 Having the same opportunities for measurements in plants could enable a better understanding of temporal changes in the phytohormonal fingerprint, provide a means of environmental monitoring and allow for easy and rapid sample collection in the field for a variety of experimental evaluations.
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